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Ancient DNA from the extinct New Zealand grayling ( Prototroctes oxyrhynchus ) reveals evidence for Miocene marine dispersal

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The evolutionary history of Southern Hemisphere graylings (Retropinnidae) in New Zealand (NZ), including their relationship to the Australian grayling, is poorly understood. The NZ grayling (Prototroctes oxyrhynchus) is the only known fish in NZ to have gone extinct since human arrival there. Despite its historical abundance, only 23 wet and dried, formalin-fixed specimens exist in museums. We used high-throughput DNA sequencing to generate mitogenomes from formalin-fixed P. oxyrhynchus specimens, and analysed these in a temporal phylogenetic framework of retropinnids and osmerids. We recovered a strong sister-relationship between NZ and Australian grayling (P. mareana), with a common ancestor ~13.8 Mya [95% highest posterior density (HPD): 6.1–23.2 Mya], after the height of Oligocene marine inundation in NZ. Our temporal phylogenetic analysis suggests a single marine dispersal between NZ and Australia, although the direction of dispersal is equivocal, followed by divergence into genetically and morphologically distinguishable species through isolation by distance. This study provides further insights into the possible extinction drivers of the NZ grayling, informs discussion regarding reintroduction of Prototroctes to NZ and highlights how advances in palaeogenetics can be used to test evolutionary hypotheses in fish, which, until relatively recently, have been comparatively neglected in ancient-DNA research.
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Zoological Journal of the Linnean Society, 2022, XX, 1–13. With 3 figures.
1
Ancient DNA from the extinct New Zealand grayling
(Prototroctes oxyrhynchus) reveals evidence for Miocene
marine dispersal
LACHIE SCARSBROOK1,2,*, KIEREN J. MITCHELL1, MATTHEW D. MCGEE3,
GERARD P. CLOSS4 and NICOLAS J. RAWLENCE1,*
1Otago Palaeogenetics Laboratory, Department of Zoology, University of Otago, Dunedin, New Zealand
2Palaeogenomics and Bio-Archaeology Research Network, School of Archaeology, University of Oxford,
Oxford, UK
3Behavioural Studies Group, School of Biological Sciences, Monash University, Melbourne, Victoria,
Australia
4Department of Zoology, University of Otago, Dunedin, New Zealand
Received 27 May 2022; revised 13 July 2022; accepted for publication 15 August 2022
The evolutionary history of Southern Hemisphere graylings (Retropinnidae) in New Zealand (NZ), including their
relationship to the Australian grayling, is poorly understood. The NZ grayling (Prototroctes oxyrhynchus) is the
only known fish in NZ to have gone extinct since human arrival there. Despite its historical abundance, only 23
wet and dried, formalin-fixed specimens exist in museums. We used high-throughput DNA sequencing to generate
mitogenomes from formalin-fixed P. oxyrhynchus specimens, and analysed these in a temporal phylogenetic
framework of retropinnids and osmerids. We recovered a strong sister-relationship between NZ and Australian
grayling (P. mareana), with a common ancestor ~13.8 Mya [95% highest posterior density (HPD): 6.1–23.2 Mya],
after the height of Oligocene marine inundation in NZ. Our temporal phylogenetic analysis suggests a single marine
dispersal between NZ and Australia, although the direction of dispersal is equivocal, followed by divergence into
genetically and morphologically distinguishable species through isolation by distance. This study provides further
insights into the possible extinction drivers of the NZ grayling, informs discussion regarding reintroduction of
Prototroctes to NZ and highlights how advances in palaeogenetics can be used to test evolutionary hypotheses in fish,
which, until relatively recently, have been comparatively neglected in ancient-DNA research.
ADDITIONAL KEYWORDS: extinction – formalin-fixed – Oligocene marine inundation – Prototroctidae
– Retropinnidae.
INTRODUCTION
The arrival of Polynesians in Aotearoa (later known
as New Zealand) around ad 1280 (Wilmshurst et al.,
2008), followed by Europeans (effectively in the late
1700s), resulted in widespread habitat modification
and many species extinctions (Tennyson & Martinson,
2007; McWethy et al., 2014; Rawlence et al., 2020).
Since human arrival, at least 70 species of birds have
gone extinct, in addition to one mammal (Rawlence
et al., 2016; Rawlence et al., 2020), one lizard (Worthy,
1987) and three frogs (Easton et al., 2021). The New
Zealand grayling Prototroctes oxyrhynchus Günther,
1870 (or upokororo) is the only freshwater fish
species known to have become extinct in New Zealand
(Fig. 1), with the last confirmed sighting in 1923 by
anthropologist Te Rangi Hīroa (Sir Peter Henry Buck),
who captured ‘over forty grayling in a funnel-shaped
net in the Waipu River in northern New Zealand
(Hīroa, 1926). Later unverified reports (e.g. newspaper
articles) suggest survival into the 1950s, and species
distribution models imply persistence as late as the
1970s (McDowall, 1990; Lee & Perry, 2019). However,
despite their former abundance, the New Zealand
grayling is now only known from 23 formalin-fixed
specimens (both stuffed skins and wet-preserved) in
*Corresponding authors. E-mail: lachiescarsbrook@gmail.com;
nic.rawlence@otago.ac.nz
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2 L. SCARSBROOK ET AL.
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
museums in New Zealand and the United Kingdom
(see: McDowall, 1976) – in-part due to the intensity of
20th century fishing practices (e.g. reports of cartloads
of graling being traded; Preston, 1986).
The life-history traits of the New Zealand grayling
are uncertain – their spawning habits are entirely
unknown, and they were reportedly cryptic, residing
in deep pools and feeding nocturnally (McDowall,
1976). Individuals commonly reached lengths of 270–
280 mm, and weighed up to 1.36 kg (McDowall, 1990).
Historically, this species inhabited both North and
South Island rivers and streams proximal to the ocean
(due to its amphidromous behaviour; McDowall, 1990),
and may have been one of ‘the most common freshwater
fish in many parts of New Zealand’ (Phillipps, 1923).
Ethnohistorical evidence suggests that the New
Zealand grayling was an important seasonal food
source for Māori (Leach, 2006; McDowall, 2011; Fyfe &
Bradshaw, 2020). However, confirmed skeletal remains
of the New Zealand grayling have not been found in
pre-European archaeological middens, although this
probably reflects a mixture of taphonomic (including
acidic soil chemistry) and excavation biases, and a lack
of comparative material [Leach, 2006; McDowall, 2011;
also see Seersholm et al. (2018) regarding galaxiids].
Overall, our understanding of the biology, ecology,
evolution and extinction of the New Zealand grayling
is incomplete and fragmentary.
The New Zealand grayling is generally considered
to be the sister-species to the endangered Australian
grayling Prototroctes maraena Günther, 1864, which
is presently restricted to south-eastern Australia
and Tasmania. Although the genus Prototroctes has
sometimes been attributed to a distinct family – the
Prototroctidae (McDowall, 1969; McDowall, 1976;
Nelson, 1994; Schwarzhans et al., 2021) – it is currently
considered to belong to a subfamily (Prototroctinae)
of Retropinnidae (Waters et al., 2002). Retropinnidae
(southern smelts and graylings) constitute a
monophyletic group sister to Osmeridae (northern
smelts; Li et al., 2010), sharing a common ancestor
~80 million years ago (Mya; Burridge et al., 2012).
Retropinnids are endemic to southern Australia and
New Zealand and constitute three genera: Retropinna
Gill, 1862 (southern smelts), Prototroctes Günther,
1864 (southern graylings) and the monotypic New
Zealand endemic Stokellia Stokell, 1941 (Johnson &
Patterson, 1996). Classification of the New Zealand and
Australian graylings as congeners is based exclusively
on morphological characteristics, with their division
into separate species based on higher counts of lateral
scale rows, vertebrae and gill rakers in P. oxyrhynchus
(McDowall, 1976). This hypothesis has not been tested
using molecular data.
The evolutionary history of graylings in New
Zealand – including the number of colonisation
events, the directionality and timing of dispersal,
and their relationship to Australian graylings – is
poorly understood. Otoliths (calcareous structures of
the inner ear) representing two species – P. modestus
Schwarzhans, 2011 and P. vertex Schwarzhans, 2011
– have been recovered from Early Miocene (18.7–
15.9 Mya) lacustrine deposits of the palaeolake
Manuherikia, located at St. Bathans (Schwarzhans
et al., 2011). Identification to Prototroctes was based
on morphological similarities to otoliths of P. maraena,
with their relationship to P. oxyrhynchus unknown
given the absence of known comparative material
(due to the dissolution of calcareous structures in
formalin and ethanol; see Supporting Information,
Fig. S1). In addition, two complete fossil fish have also
been recovered from a Late Pleistocene lacustrine
deposit on the north-eastern North Island (0.71–0.62
Mya), assigned to P. oxyrhynchus on the basis of
caudal fin morphology (McDowall et al., 2006; but see:
Schwarzhans et al., 2011). However, as the temporal
Figure 1. The extinct New Zealand grayling (Prototroctes oxyrhynchus). Artwork by Frank Edward Clarke. Annotations in
figure contain a nomen nudum. Museum of New Zealand Te Papa Tongarewa CC BY-NC-ND 4.0.
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NEW ZEALAND GRAYLING PHYLOGENY 3
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
origin of P. oxyrhynchus is unknown, it is not possible
to test whether these fossil taxa are likely to represent
either stem or crown members of Prototroctes – the
fossils from New Zealand could represent an ancient
(perhaps Gondwanan) and endemic lineage that
includes P. oxyrhynchus or, alternatively, an extinct
stem lineage, with P. oxyrhynchus descending from a
recent and independent dispersal (facilitated by the
juvenile marine phase of graylings).
Molecular data (i.e. ancient DNA) could help answer
several questions about the taxonomic affinities and
evolutionary origins of the New Zealand grayling.
Unfortunately, the success of ancient DNA studies
on historical formalin-fixed ‘wet’ (i.e. preserved in
fluid) and ‘dried’ (e.g. mounted) museum specimens
– which encompass most teleost specimens, New
Zealand grayling included – has historically been
highly variable (Friedman & Desalle, 2008; Garrigos
et al., 2013; Pierson et al., 2020; Pyron et al., 2022),
especially due to frequent uncertainties surrounding
early curatorial practices (e.g. changes to preservative
fluids, most commonly unbuffered formalin to
ethanol). While palaeogenetic studies focusing on fish
are becoming more common (for review see: Oosting
et al., 2019), the majority of studies to date have
focused on sequencing ancient DNA from bone (e.g.
Ferrari et al., 2021; Martinez-Garcia et al., 2021, 2022)
and not formalin-fixed tissue. Obtaining ancient DNA
from formalin-fixed specimens has been challenging,
as fixation in formalin rapidly degrades DNA (through
fragmentation and base pair modification) and
promotes cross-linkage both within and between DNA
molecules, as well as to cellular proteins; both of which
accumulate linearly with increased preservation
time (Hykin et al., 2015; Hahn et al., 2022). However,
methodological and technological advancements
– especially the advent of high-throughput DNA
sequencing – have dramatically improved success
rates of obtaining genetic data from such fluid-
preserved specimens. For example, Scarsbrook et al.
(2022) combined DNA extraction methods optimised
for ultra-short fragments (Dabney et al., 2013), single-
stranded library preparation (which breaks molecular
cross-links through heat-denaturation; Gansauge
et al., 2017) and hybridisation capture-enrichment
(González-Fortes & Paijmans, 2019) to successfully
obtain complete mitochondrial genomes from historical
‘wet’ preserved New Zealand geckos.
In this study, we used palaeogenetic techniques
to obtain mitochondrial genome sequences from
three New Zealand grayling specimens, which were
compared to a newly generated mitochondrial genome
from the Australian grayling, in addition to published
data from other retropinnid and osmerid species. These
data were used to test whether P. oxyrhynchus is most
closely related to P. maraena, to estimate the age of
the common ancestor of P. oxyrhynchus and its nearest
living relative, and to investigate genetic structuring
of P. oxyrhynchus populations within New Zealand.
We also discuss the implications of our findings for
(1) understanding the cause(s) of the extinction of the
New Zealand grayling, and (2) informing discussion
regarding the possible re-introduction of Prototroctes
to New Zealand.
MATERIAL AND METHODS
australian grayling mitochondrial genome
sequencing
Two live P. maraena individuals were provided via
Wayne Koster (Department of Environment, Land,
Water & Planning; Victoria, Australia), transported
to Monash University and euthanised with clove oil.
All procedures involving live fish were performed
under project AE17725 to co-author MDM at Monash
University. Genomic DNA was immediately extracted
from muscle tissue using a Qiagen Blood and Tissue
kit, following the manufacturer’s instructions for
animal tissue. DNA was sequenced by a commercial
provider (Deakin Biosciences) using a polymerase
chain reaction (PCR)-free protocol for 2 × 150 bp
(paired-end) sequencing on an Illumina NovaSeq S4
flow cell. The first 500 000 read pairs were extracted
using bbduk.sh in the BBTools package (http:/
sourceforge.net/projects/bbmap) and the mitochondrial
genome assembled using tadpole.sh at a kmer size of
25. Mitochondrial genes and RNAs (rRNAs/tRNAs)
were annotated using mitoFinder v.1.4 (Allio et al.,
2020) under default parameters, with the Retropinna
semoni (Weber, 1895) (NCBI KX421785) mitochondrial
genome used as a reference.
australian grayling cytochrome b sequencing
Genomic DNA was extracted in the modern
evolutionary genetics laboratory in the Department
of Zoology (University of Otago), from P. maraena
tissue samples (fin-clips) obtained from contemporary
populations in Victoria (Bunyip River; N = 5) and
Tasmania (N = 1). Specifically, tissue samples
(~2 mm2) were added to 400 μL resuspended ‘Chelex
Solution’ (2.5 g Chelex 100; 50 mL dH2O) and 2 μL
Proteinase-K (20 mg/mL) and incubated at 60 °C for
24 h at 600 rpm (on a thermoshaker). Tubes were then
heated at 90 °C for 8 min (on a heating block), followed
by centrifugation for 10 min at 13 000 rpm. A 1273 bp
fragment of the mitochondrial protein-coding gene
cytochrome b (Cytb) and associated tRNA-Thr was
amplified using the following primer combination –
forward: HYPSLA (5 GTG GCT TGA AAA ACC ACC
GTT 3; Thacker et al., 2007); reverse: Ret.Thr31 (5
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4 L. SCARSBROOK ET AL.
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
CTC CAA CCT CCG ACT TAC AAG 3; Page & Hughes,
2010). PCRs (10 μL) contained 1 × AmpliTaq Gold
Buffer, 0.75 mmol/L MgCl2, 0.25 mmol/L dNTPs, 0.5
U AmpliTaq Gold DNA polymerase (ThermoFisher),
1 μmol/L each primer (HYPSLA/Ret.Thr31) and 1 μL
template DNA. Amplification was performed on an
Eppendorf ProS Mastercycler (‘thermocycler’) under
the following conditions: an initial denaturation of
94 °C for 3 min; 40 cycles of 94 °C for 30 s, 52 °C for
1 min and 72 °C for 2 min, with a final extension of
72 °C for 10 min. Resulting amplicons were visualised
using gel electrophoresis (0.5 g agarose; 25 mL 1 × TAE
Buffer; 0.5 μL SYBRsafe) and purified using ExoSap
[1 μL Shrimp Alkaline Phosphatase and 1.5 μL diluted
(1:20) Exonuclease I; ThermoFisher], incubated at
37 °C for 30 min followed by 95 °C for 5 min on a
thermocycler. Purified amplicons were bidirectionally
Sanger sequenced on an ABI 3730xl DNA Analyzer
(University of Otago Genetic Analysis Service) using
BigDye terminator technology. Chromatogram trace
files were edited (i.e. primer and poor-quality base
trimming, ambiguous base-calling) in 4Peaks v.1.8
(https://nucleobytes.com/4peaks/index.html).
ancient dna analysis oF the extinct new
Zealand grayling
Palaeogenetic work was conducted in the dedicated
Otago Palaeogenetics Laboratory in the Department
of Zoology (University of Otago). Ancient DNA was
extracted from either ‘dried’ scales or ‘wet’ tissue from
formalin-fixed historical P. oxyrhynchus specimens
from New Zealand museum collections (N = 12; see
Supporting Information, Table S1) using the QIAamp
DNA FFPE Tissue Kit, following the manufacturer’s
instructions (excluding the xylene paraffin removal
step). This method utilises a heat denaturation step
(at 90 °C) following tissue lysis to remove molecular
cross-links, characteristic of DNA from formalin-fixed
tissues (Hykin et al., 2015). Single-stranded Illumina
sequencing libraries were generated from the ancient
DNA extracts (following an adapted protocol; Scarsbrook
et al., 2022) to enhance recovery of highly fragmented
and altered DNA cross-linked to proteins (Gansauge &
Meyer, 2013). Optimal cycle number (No) for the indexing
of single-stranded libraries was determined through
quantitative PCR (qPCR), to reduce clonality and limit
heteroduplex formation (Gansauge et al., 2020). qPCRs
(10 μL) were performed using 1 × Maxima SYBR Green
qPCR Master Mix (Thermo Scientific), 0.2 mol/L each of
IS7 and IS8 primers (IS7: 5 ACA CTC TTT CCC TAC
ACG AC 3; IS8: 5 GTG ACT GGA GTT CAG ACG TGT
3) and 1 μL of diluted (1:10) library on a QuantStudio 5
Real-Time PCR System as follows: 95 °C for 10 min; 40
cycles of 95 °C for 30 s, 60 °C for 30 s and 72 °C for 30 s.
Full-length P5/P7 adapters containing unique 7-mer
barcode combinations were added to libraries through
quadruplicate indexing PCRs (to maximise complexity).
Indexing PCRs (25 μL) were performed using 1 × High
Fidelity PCR Buffer (Invitrogen), 2 mmol/L MgSO4,
0.25 mmol/L dNTPs, 1.25 U Platinum Taq DNA
polymerase High Fidelity (Invitrogen), 0.5 mol/L P5/P7
indexing primers and 5 μL library on a thermocycler
as follows: 94 °C for 12 min; No cycles of 94 °C for 30 s,
60 °C for 30 s and 72 °C for 45 s; 72 °C for 10 min.
Replicate indexed libraries were pooled, purified
using AMPure XP (Agencourt) at 1.1 × bead:template
ratio (following the manufacturer’s instructions) and
quantified using a Qubit dsDNA High Sensitivity Assay
kit (ThermoFisher).
Endogenous mitochondrial DNA was selectively
enriched through in-solution hybridisation-capture
(following an adapted protocol; Scarsbrook et al.,
2022), with biotinylated baits generated from sheared
mitochondrial amplicons of the New Zealand smelt
Retropinna retropinna Richardson, 1848. Specifically,
high-molecular weight (HMW) DNA was extracted from
the high-quality tissue (liver) sample of a R. retropinna
using the MagMAXTM DNA Multi-Sample Ultra 2.0
Kit (ThermoFisher), following the manufacturer’s
instructions for saliva or whole blood. The complete
R. retropinna mitochondrial genome (~16.5 kb) was
amplified (in a single fragment) through long-range
‘shuttle’ PCR using the following primer combination:
forward: S-LA-16S-L (5 CGA TTA AAG TCC TAC
GTG ATC TGA GTT CAG 3; Miya & Nishida, 2000);
reverse: S-LA-16S-H (5 TGC ACC ATT RGG ATG
TCC TGA TCC AAC ATC 3; Miya & Nishida, 2000).
Long-range ‘shuttle’ PCR (50 μL) was performed
using 1 × PrimeSTAR GXL Buffer, 200 mol/L dNTPs,
1.25 U PrimeSTAR GXL DNA Polymerase (Takara),
0.2 mol/L each primer (S-LA-16S-L/S-LA-16S-H)
and ~100 ng HMW DNA extract, on a thermocycler
as follows: 30 cycles of 98 °C for 10 s and 68 °C for
16 min. The resulting amplicon was visualised using
gel electrophoresis (0.5 g agarose; 25 mL 1 × TAE
Buffer; 0.5 μL SYBRsafe) and sheared to 150–300 bp
using a Picoruptor (Diagenode) sonicator with 13
cycles of: 30 s on, 30 s off, at 4 °C. Sheared amplicons
were purified using AMPure XP magnetic beads
(Agencourt) at 1.8 × bead:template ratio (following the
manufacturer’s instructions), quantified using a Qubit
dsDNA Broad Range Assay kit (ThermoFisher) and
used to generate biotinylated baits (see above).
Post-capture re-amplification PCRs (25 μL)
were performed using 1 × AmpliTaq Gold Buffer
(ThermoFisher), 2.5 mmol/L MgCl2, 0.25 mmol/L dNTPs,
1.25 U AmpliTaq Gold DNA polymerase (ThermoFisher),
0.5 mol/L each primer (IS5: 5 AAT GAT ACG GCG ACC
ACC GA 3, IS6: 5 CAA GCA GAA GAC GGC ATA CGA
3) and 5 μL post-capture library on a thermocycler as
follows: 94 °C for 12 min; Nno cycles (as above) of 94 °C
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NEW ZEALAND GRAYLING PHYLOGENY 5
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
for 30 s, 60 °C for 30 s and 72 °C for 45 s; 72 °C for 10 min.
Reamplified libraries were purified and quantified (as
above) for equimolar pooling. Mean fragment size of the
captured libraries was measured on a QIAxcel Advanced
System using a 25 bp–10 kb alignment marker; with
raw data calibration and visualisation performed using
QIAxcel scre enge l v.1.6.0 (Qiagen). Each library
was diluted to 10 nmol/L and run on an Illumina
NextSeq (Garvan Institute of Medical Research) using
2 × 75bp (paired-end) sequencing chemistry and custom
sequencing primers (CL72: 5 ACA CTC TTT CCC TAC
ACG ACG CTC TTC C 3; G’stein: 5 GGA AGA GCG
TCG TGT AGG GAA AGA GTG T 3).
Reads were demultiplexed using saBre v.1.0 (https://
github.com/najoshi/sabre) with no mismatches allowed
(-m: 0). Adapter sequences were removed and paired-end
reads collapsed using adaPterremoval v.2.3.1 (Schubert
et al., 2016), with a mismatch rate of 0.33 (-mm: 3). Low-
quality bases (Phred Quality Score < 30) were trimmed
(--minquality: 30; --trimns) and collapsed reads shorter than
25 bp discarded (-minlength: 25). To ensure the effective
removal of adapters, read quality was visualised using
Fastqc v.0.11.9 (https://www.bioinformatics.babraham.
ac.uk/projects/fastqc/). Mitochondrial sequence alignments
were generated from collapsed reads using the BAM
pipeline implemented in PALEOMIX v. 1.2.14 (Schubert
et al., 2014). Briefly, collapsed reads were mapped against
an Australian grayling (Prototroctes maraena) reference
mitochondrial genome (this study) using Bwa v.0.7.17
(-n: 0.01; -o: 2; Li & Durbin, 2009). samtools v.0.1.19
(Li et al., 2009) was used to select reads with a mapping
Phred Quality Score > 25 (-q: 25), with duplicate reads
discarded in Picard v.2.1.0 (http://broadinstitute.github.io/
picard/) using the MarkDuplicates.jar tool. Misalignments
from reads overlapping indels were improved using
the IndelRealigner tool implemented in gatk v.4.1.4.1
(McKenna et al., 2010). Finally, to ensure ancient DNA
authenticity, characteristic damage patterns (i.e. nucleotide
mis-incorporation and DNA fragmentation;Supporting
Information, Fig. S2) were assessed using maPdamage
v.2.0.8 (Ginolhac et al., 2011; Jónsson et al., 2013). Majority
consensus sequences (75%) were generated for each BAM
alignment in geneious Prime v.2021.2.2, with bases
only called at sites covered by 3 reads (with IUPAC
ambiguities otherwise called). Mitochondrial genomes
were annotated using the MITOS Webserver (Bernt et al.,
2013), and manually verified, to determine the location
and size of protein-coding genes and tRNAs/rRNAs.
Phylogenetic analysis
Prototroctes oxyrhynchus and P. maraena mitochondrial
genomes were aligned against published retropinnid
and osmerid sequences (Supporting Information,
Table S2) using MUSCLE v.3.8.425 (using ‘default’
parameters; Edgar, 2004) implemented in geneious
Prime v.2021.2.2 (Biomatters; https://www.geneious.
com/). Cytochrome b (1142 bp) was extracted (in
geneious Prime ) from the mitochondrial genome
alignment and aligned against both modern P. maraena
samples (N = 7; GenBank accession numbers:
ON161129–ON161135) and published retropinnid
sequences (N = 128; Supporting Information, Table
S2). 16S rRNA (1642 bp) was similarly extracted
and aligned against published sequences (N = 15;
Supporting Information, Table S2). Median-joining
haplotype networks (Bandelt et al., 1999) were
constructed from both 16S and Cytb alignments in
PoPart (Leigh & Bryant, 2015).
Topology estimation and molecular dating were
performed under a Bayesian framework in BEAST
v.1.8.4 (Drummond et al., 2012) using the mitochondrial
genome alignment (subsampled to include only the
most complete P. oxyrhynchus sequence: ON220596).
Data were analysed as four partitions, using best-fitting
substitution models identified using the Bayesian
information criterion in PartitionFinder v.1.0.1
(Lanfear et al., 2012): first-codon positions of H-strand
encoded protein-coding genes (GTR+I+G), second-
codon positions of H-strand encoded protein-coding
genes (GTR+I), first-codon positions of ND6 (TrN+G),
and second-codon positions of ND6 (K81+I). We applied
a birth–death tree prior and uncorrelated log-normal
relaxed clock model (with rate multiplier parameters
for each partition). The continuous-time Markov chain
scale reference prior (Ferreira & Suchard, 2008) was
applied to the mean rate parameter. We constrained
the age of the time to most recent common ancestor
(TMRCA) of the Osmeridae according to a log-normal
distribution with a hard minimum at 57 Mya, mean
of 13.85 and standard deviation of 1.0 (such that 95%
of the prior distribution fell between 57 and 100.5
Mya). The minimum age was based on the oldest
known fossil osmerid Speirsaenigma lindoei Wilson &
Williams, 1991 from the Palaeocene of Canada (Wilson
& Williams, 1991). The maximum age was based on
the absence of crown osmerids from Late Cretaceous
fossil localities (Burridge et al., 2012). The mean and
standard deviation were chosen to reflect Burridge
et al.’s (2012) posterior estimate for the equivalent
node (based on a larger dataset with additional fossil
age constraints). Other priors were set to their default
values. We ran three Markov chain Monte Carlos
(MCMCs) for 50 million generations each, sampling
trees and parameters every 5000 generations. The
first 10% of each chain was removed as burn-in and
remaining data were combined using logcomBiner
v.1.8.4. TRACER v.1.7.1 (Rambaut et al., 2018) was used
to monitor parameter values, ensuring convergence
and effective sample sizes > 200. A maximum clade
credibility tree was generated in treeanno tat or
v.1.8.4 and visualised in Figtree v.1.4.4.
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RESULTS
ancient mitochondrial genomes
Mitochondrial genomes (16 591 bp) were successfully
recovered from three of the 12 formalin-fixed historical
New Zealand grayling (Prototroctes oxyrhynchus)
specimens – in each instance, samples consisted of
scales derived from dried specimens, which are an
excellent source of endogenous DNA (Pinsky et al.,
2021). Alignments produced one complete (ON220596)
and two partial (ON220594–5) sequences, containing
between 1310 and 3659 unique mapping reads covering
79.8–96.2% of the reference sequence to at least
three-fold depth of coverage (3.6–10.8×; Supporting
Information, Table S3). Characteristic short fragment
lengths (47.7–51.4 bp; Supporting Information,
Table S3) and damage patterns (i.e. increased C-to-T
substitution frequencies at read ends) authenticated
recovered DNA sequences as ancient (Supporting
Information, Fig. S2). The remaining, predominantly
wet-preserved (i.e. formalin-fixed) specimens yielded
few mapped reads (0–115; Supporting Information,
Table S3).
Phylogenetic analysis
Our time-calibrated Bayesian phylogeny (Fig. 2) was
well resolved, with the majority of branches receiving
unequivocal support (i.e. posterior probabilities = 1.0).
Divergence of the Retropinnidae and Osmeridae
occurred 129.3 Mya (95% HPD: 83.5–183.6 Mya), with
crown-ages of each family estimated at 70.4 Myr (95%
HPD: 40.3–105.7 Myr) and 67.0 Myr (95% HPD: 57.2–
85.9 Myr), respectively. Within Retropinnidae, the
genus Prototroctes was the sister-taxon to Retropinna,
with the extant P. maraena and extinct P. oxyrhynchus
diverging 13.8 Mya (95% HPD: 6.1–23.2 Mya).
Conversely, earlier lineage separation was inferred
within the genus Retropinna, with divergence between
R. retropinna and R. semoni estimated at 57.0 Mya
(95% HPD: 30.6–87.4 Mya).
Cytochrome b and 16S rRNA haplotype networks
(Fig. 3) revealed no evidence for population structure
(or cryptic taxonomic diversity) in P. oxyrhynchus, with
all individuals sharing the same haplotype. Conversely,
two distinct haplotypes were observed in P. maraena,
however these were not geographically structured,
with both haplotypes present in the same population
(for Cytb; Fig. 3A).
DISCUSSION
grayling Phylogeny and BiogeograPhy
Our phylogenetic results and node age estimates among
extant taxa are concordant with the results of previous
studies (e.g. Burridge et al., 2012; Straube et al., 2018).
However, our new data allow us to include the extinct
New Zealand grayling in a molecular phylogeny for the
first time – our results unequivocally support a sister-
lineage relationship between the New Zealand and
Australian graylings, and suggest that the common
ancestor of the two species occurred 6.1–23.2 Mya (Fig.
1). This divergence timing is comparable to the age of
splits between osmerid sister-pairs in our analysis
(see Fig. 1), and pre-dates the most-recent common
ancestor of the two R. semoni individuals included in
our alignment, which probably represent two different
species (with one or both belonging to an undiagnosed
cryptic species; Hammer
et al., 2007; Hughes et al., 2014;
Schmidt et al., 2016). Consequently, it is clear that the
New Zealand and Australian graylings represent two
distinct species, consistent with previously observed
morphological differences (McDowall, 1976). Further,
extensive genetic distance between Prototroctes
species and the remaining Retropinnidae (see Fig. 2)
is consistent with previous assertions of subfamily-
level (e.g. Prototroctinae) – but not family-level (e.g.
Prototroctidae) – distinction of Southern Hemisphere
graylings.
Extant retropinnids are restricted to south-eastern
Australia and New Zealand, but a possible fossil
retropinnid – with closest affinities to Prototroctes
– has also been described from the Miocene of Chile
(Navidadichthys miru Schwarshans & Nielsen, 2021;
Schwarzhans & Nielsen, 2021). This exclusively
Southern Hemisphere distribution suggests that
Gondwanan vicariance may have played a role in
determining the distribution of retropinnid lineages.
Our estimate for the age of the common ancestor of
R. semoni and R. retropinna (30.6–87.4 Mya) is broadly
consistent with this hypothesis – the distribution
of these two lineages in Australia and New Zealand
may have been driven by rift-related separation
of these respective continental blocks through the
opening of the Tasman Sea (52–85 Mya; Cooper &
Millener, 1993). However, our results for P. maraena
and P. oxyrhynchus suggest that marine dispersal,
not Gondwanan vicariance, was the driver of their
respective distributions in Australia and New Zealand.
While our results implicate marine dispersal
in Prototroctes – made highly plausible by the
amphidromous life cycle of graylings – they are
equivocal on the pre-Miocene distribution of the
grayling lineage. Dispersing individuals could have
originated from New Zealand, Australia or even South
America (since fossil data indicate that this lineage was
present in Chile during the Miocene). While P. modestus
and P. vertex are known from New Zealand’s St. Bathans
assemblage (Schwarzhans et al., 2011), the age of these
fossil deposits (18.7–15.9 Mya) overlaps with our
estimate for the divergence between P. maraena and
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NEW ZEALAND GRAYLING PHYLOGENY 7
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
P. oxyrhynchus. Consequently, P. modestus and P. vertex
could represent early members of the lineage leading
to P. oxyrhynchus, and do not necessarily indicate pre-
Miocene presence of graylings in New Zealand. If so, our
age estimates suggest that colonisation of New Zealand
by graylings might have occurred only once, after the
height of the Oligocene marine transgression (27–22
Mya) during which > 80% of continental New Zealand
(i.e. Zealandia) was submerged (Mildenhall et al., 2014).
The extent and distribution of freshwater habitats in
New Zealand would have been severely reduced (if not
entirely absent) during this time, possibly resulting in
Figure 2. Time-calibrated Bayesian phylogeny of the Osmeriformes (Retropinnidae and Osmeridae) constructed from first
and second codon positions of all 13 mitochondrial protein coding genes. 95% highest probability density (95% HPD) of the
age estimate for each node is indicated by horizontal grey bars, with Bayesian posterior probabilities of 1.0 represented
by white circles (otherwise values are reported). The x-axis represents time in millions of years before present (Mya). Red
circles denote phylogenetic position and age of described retropinnid fossil material: Prototroctes modestus and P. vertex
(18.7–15.9 Myr; Schwarzhans et al., 2011), Navidadichthys mirus (18–17 Myr; Schwarzhans et al., 2021), Prototroctes
oxyrhynchus (0.71–0.62 Myr; McDowall et al., 2006) – we also indicate Speirsaenigma lindoei (57 Myr; Wilson & Williams,
1991), which was used to constrain the minimum age of crown Osmeridae. Timing of relevant geological events, such as
rifting of the Zealandian and Australian continental blocks (Cooper & Millener, 1993) and maximum marine inundation (i.e.
‘Oligocene drowning’; Mildenhall et al., 2014) are highlighted. Continental distribution of retropinnid lineages are indicated
by outline maps. Extinct taxa are denoted †.
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8 L. SCARSBROOK ET AL.
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
the extinction and turnover of many freshwater animal
lineages. Concomitant expansion of freshwater habitats
in the Early Miocene (e.g. Lee et al., 2007; Schwarzhans
et al., 2011) might have provided opportunities for
colonisation and/or diversification that were previously
limited by density-dependent founder-takes-all
processes (Waters et al., 2013). Indeed, the respective
common ancestors of two clades of galaxiid fishes found
in New Zealand also date to the Late Oligocene or
Early Miocene, where similar processes are implicated
(Burridge et al., 2012; Burridge & Waters, 2020).
grayling extinction
The drivers of the extinction of the New Zealand
grayling are debated. Reductions in population size
and geographic distribution were identified shortly
after European arrival in New Zealand, with concerns
raised as early as the 1870s (Rutland, 1877; Allen,
1949). By the early 1920s, the New Zealand grayling
was rare and restricted to isolated rivers and streams
away from human settlement (Phillipps, 1923; Allen,
1949), but it did not receive government protection
until 1952, and was officially declared extinct in
2002 (Hitchmough, 2002). This decline and eventual
extinction has been variously attributed to: (1)
overfishing; (2) the introduction of trout, resulting
in direct predation or transfer of disease (e.g. fungus
and parasites), which has caused epidemics in
Australian grayling populations (e.g. Johnston, 1882;
Saville-Kent, 1887; Kaminskas, 2021); and/or (3)
environmental modification and habitat degradation
(Allen, 1949). Some authors have suggested that the
disappearance of grayling from pristine unmodified
rivers indicates that habitat degradation was not
a primary cause of extinction (McDowall, 1990), but
other authors note that source-sink dynamics could
cause indirect depletion of populations, even in these
pristine habitats, as individuals migrate to the lower
density degraded habitats (Lee & Perry, 2019).
Lee and Perry (2019) suggested that up to 30% of
grayling per generation could have been sustainably
harvested in the absence of source-sink dynamics,
reducing to only 5% when considered a single
panmictic meta-population in the presence of source-
sink dynamics. The presence or absence of source-sink
dynamics is theoretically testable using genetic data
– marked phylogeographic structure, as observed in
Australian smelt (Hughes et al., 2014) and suggested by
colour variation in New Zealand grayling across their
range (McDowall, 1990), would imply that source-sink
dynamics were not operating over large distances. We did
not observe deep divergences among our three samples
(Fig. 2), but these individuals were only drawn from two
South Island localities (the Clutha and Hokitika rivers
on opposite sides of the Southern Alps) – as attempts to
extract ancient DNA from other (mostly ‘wet’) grayling
specimens from throughout New Zealand were not
successful. However, our results suggest that additional
sampling, especially of North Island individuals (e.g.
Whanganui Regional Museum), combined with more
specialised molecular techniques – optimised for
Figure 3. Median-joining haplotype networks of the Retropinnidae constructed from A, cytochrome b (1363 comparable
sites) and B, 16s rRNA (575 comparable sites) alignments in PoPart (for GenBank Accession numbers, see Supporting
Information, Table S2). Haplotypes (circles) are proportional to frequency (numbers), with number of substitutions indicated
by hatches along branches. Black circles represent undetected intermediary haplotypes, with colours corresponding to
species.
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NEW ZEALAND GRAYLING PHYLOGENY 9
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
the recovery of highly degraded ancient DNA from
formalin-fixed specimens (especially for ‘wet’ specimens;
e.g. Campos & Gilbert, 2012; Dabney et al., 2013;
Straube et al., 2021; Hahn et al., 2022) or dried fish scales
– could yield additional mitochondrial (and potentially
nuclear) genomes from New Zealand grayling. These
data would allow the presence of source-sink dynamics
to be more effectively evaluated and provide insight
into the importance of different drivers in the extinction
of the New Zealand grayling.
restoring lost ecological Functions to rivers
By introducing australian grayling to new
Zealand
Historical reports suggest that New Zealand grayling
were omnivorous, feeding on small invertebrates and
algae (McDowall, 1990). As such, they probably occupied
an ecological feeding niche unlike any other current
extant native freshwater fish species (McDowall, 1990),
and hence their (likely) extinction has resulted in some
degree of lost ecological function in rivers where New
Zealand grayling were formerly abundant (McDowall,
1990). Where a species translocation to restore lost
ecological function is planned, the target species
for translocation should be both functionally and
genetically as close as possible to the species that was
originally lost (Armstrong & Seddon, 2008). Based on
our analysis, the Australian grayling may be the most
likely extant candidate species to fulfil this criterion,
pending further palaeoecological (e.g. stable dietary
isotopes; Durante et al., 2020; Welicky et al., 2021),
morphometric and functional palaeogenomic research.
That said, our work also confirms that New Zealand
and Australian grayling are distinct species; hence the
translocation of Australian grayling to replace the New
Zealand grayling is clearly a species introduction (i.e.
ecological surrogate), not a reintroduction (Armstrong
& Seddon, 2008). Whilst this point might seem to be
mere semantics, the distinction does serve to highlight
the potential challenges of such a management step.
Given the time since their last common ancestor, the
two species would have probably diverged in a variety
of key morphological and behavioural traits, thus
predicting how Australian grayling would respond to
New Zealand conditions is impossible, both in terms
of the viability of such an introduction, but also with
respect to the goal of restoring lost ecological function.
ACKNOWLEDGEMENTS
We thank Tom Trnski and Severine Hannam (Auckland
War Memorial Museum); Paul Scofield (Canterbury
Museum); Karen Cook (Fish and Game, Nelson); Andrew
Stewart, Jeremy Barker and Clive Roberts (Museum of
New Zealand Te Papa Tongarewa); Eimear Egan (National
Institute of Water and Atmospheric Research); and Kane
Fleury and Emma Burns (Otago Museum) for access
to P. oxyrhynchus material for genetic analysis; James
Maclaine (Natural History Museum, United Kingdom)
for generating X-ray images of NMUK P. oxyrhynchus
syntypes; Chris Burridge (University of Tasmania), Matt
Jarvis (University of Otago) and Wayne Koster (Arthur
Rylah Institute for Environmental Research) for access
to fin-clips and otoliths from contemporary Australian
grayling (P. maraena) populations; Jesse Wansbrough
(University of Otago) for providing the R. retropinna tissue
sample; and Alex Verry and Tania King (University of
Otago) for their assistance in optimising DNA extraction,
PCR and next-generation sequencing protocols. We
also acknowledge the use of New Zealand eScience
Infrastructure (NeSI) high-performance computing
facilities as part of this research. We acknowledge that
Māori, the indigenous people of Aotearoa New Zealand,
have kaitiakitanga (guardianship) over the organisms
from their rohe (tribal area).
FUNDING
Funding was provided by the University of Otago.
DATA AVAILABILITY
The data that support the findings of this study are
openly available, with consensus mitochondrial genomes
openly available in GenBank (Accession Numbers:
ON161129–ON161135; ON220594–ON220597).
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SUPPORTING INFORMATION
Additional Supporting Information may be found in the online version of this article at the publisher’s website.
Figure S1. X-ray images of New Zealand grayling (Prototroctes oxyrhynchus) specimens at the British National
History Museum (NHM), used to assess preservation of calcareous otoliths. Images were generated by James
Maclaine (NHM). Top to bottom: 1870.5.22.17 (syntype); 1870.5.22.18 (syntype); 1873.12.13.69; 1886.11.18.80;
1935.3.14.65.
Figure S2. MapDamage reports for mapped collapsed reads of historic New Zealand grayling (Prototroctes
oxyrhynchus) single-stranded libraries (NIWA1, NIWA2, OMVT2922). The left panels show characteristic high
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NEW ZEALAND GRAYLING PHYLOGENY 13
© 2022 The Linnean Society of London, Zoological Journal of the Linnean Society, 2022, XX, 1–13
frequency of purines (A and G) at read termini (top) and accumulation of 5 C to T (red curve) misincorporations
(bottom), which authenticate ancient DNA. The right panel shows characteristic short fragment length of single-
end mapped reads (top).
Table S1. Sample information for New Zealand grayling (Prototroctes oxyrhynchus) specimens including:
institution [Auckland War Memorial Museum (AWMM), Canterbury Museum (CM), Museum of New Zealand
Te Papa Tongarewa (NMNZ), Otago Museum (OM)], sample identification (ID), tissue type and locality. The last
confirmed sighting of New Zealand grayling was in 1923.
Table S2. GenBank Accession numbers for Retropinnidae (R) and Osmeridae (O) sequences used in phylogenetic
analyses. * denotes sequences derived through annotation extraction from complete mitochondrial genomes.
Bolded accession numbers indicate sequences generated in this study.
Table S3. Mitochondrial genome assembly statistics for historic New Zealand grayling (Prototroctes
oxyrhynchus) specimens (see Supporting Information, Table S1) with reads generated through single-stranded
library preparation. Summary statistics are not reported (denoted by ‘-’) for ‘GC content (%)’, ‘Ambiguous Sites’,
‘Ambiguous bases (%)’, ‘Reference sequence coverage (%)’ and ‘Contig length (bp)’ in the majority of individuals
given insufficient reference sequence coverage.
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... These collections can be used to resolve taxonomic questions, monitor species that are relevant to public health and safety concerns, track the history and progress of biological invasions, and measure organismal responses to global change (Suarez and Tsutsui 2004;Winker 2004;Watson and Werb 2013;Holmes et al. 2016). Additionally, the worldwide acceleration of extinction events, particularly in freshwater ecosystems (Jelks et al. 2008;Burkhead 2012;Closs et al. 2016), has further enhanced the value of phylogenetic and population genetic research using preserved specimens of rare or declining species (Burrell et al. 2015;Splendiani et al. 2017;Gaither and DiBattista 2022;Scarsbrook et al. 2023). In combination with the monitoring of extant populations, the analysis-including genetic examinations-of specimens housed in natural history collections can play an important role in conservation status assessments and informing management actions (Shaffer et al. 1998;Winker 2004;Sutherland et al. 2009;Lister et al. 2011;Watson and Werb 2013;Holmes et al. 2016;Hahn et al. 2021). ...
... The use of a heated alkali treatment on formalin-preserved tissues can break cross-links that formed during preservation, and the addition of prescribed tissue washes can remove excess formalin from the sample (Hykin et al. 2015;Splendiani et al. 2017;Billerman and Walsh 2019;Rocha et al. 2022). These methods have been successful in recovering DNA from specimens of several marine fish species (Zhang 2010;Hagedorn et al. 2018;Burrows et al. 2019;Jalenques et al. 2021;Agne et al. 2022;Scarsbrook et al. 2023) but have yet to be applied to many groups of freshwater fishes, including lampreys (order ...
... Preceding the heated alkali treatment with a series of glycine-tris-EDTA (GTE) buffer washes may more efficiently cleave cross-linkage complexes and bind excess formalin to improve extract quality (Splendiani et al. 2017;Billerman and Walsh 2019;Rocha et al. 2022;Scarsbrook et al. 2023). A standard protocol was used for tissue washes that requires three sequential buffer washing steps following Hykin et al. (2015). ...
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