Saving Freshwater Pearl Mussels from Extinction through Captive Breeding
Submitting Institution
Queen's University BelfastUnit of Assessment
Earth Systems and Environmental SciencesSummary Impact Type
EnvironmentalResearch Subject Area(s)
Environmental Sciences: Environmental Science and Management
Biological Sciences: Ecology
Agricultural and Veterinary Sciences: Fisheries Sciences
Summary of the impact
UK Species Action Plans (SAP) and selection of Special Areas of
Conservation under the EC Habitats Directive for declining populations of
the critically endangered freshwater pearl mussel Margaritifera
margaritifera were informed by QUB research. As an element of the
Northern Ireland SAP, in 2009 about 350 mussels produced in a unique
captive-breeding facility at a fish farm were released into a river where
mussels face extinction. Up to 99% of released mussels survived and a
further 240 additional juveniles were released in 2013. This approach
complements policy for habitat restoration through catchment management,
was a first in Europe and is now being emulated for endangered populations
in Austria.
Underpinning research
Context: Freshwater pearl mussels (Margaritifera margaritifera),
which can live for over 100 years, have a life cycle phase parasitic on
fish gills and require clean water. Large populations of mussels, which
can help maintain river water quality, have or will shortly become extinct
in parts of Europe and North America due to impacts such as pearl-fishing
and siltation from land drainage and run-off from agriculture and
forestry. The species is included in Annexes II and IV of the EC Habitats
Directive (92/43/EEC) and Appendix II of the Bern Convention. Failure of
EU member states to protect remaining populations risks their exposure to
large infraction fines. The freshwater pearl mussel has been described as
a flagship species because measures taken to ensure its survival have
broader environmental benefits.
QUB research: Research on the status and distribution of pearl
mussels in the mid to late 1990s evidenced their decline and predicted
extinction in the north of Ireland (Dai Roberts with research students Tim
Mackie and Colin Beasley).1,2 Populations in rivers that
historically supported hundreds of thousands of mussels had declined to
hundreds or a few thousand, dominated by older individuals, with little
evidence of recruitment. Our predictions of local extinctions, based on
life expectancies of the youngest individuals, have been reinforced by
recent research (Roberts and research student Conor Wilson 2007-2010)
modelling extinction trajectories for mussel populations in England,
Scotland, Wales and Ireland.4 Protection of wild populations of
pearl mussels is unlikely itself to lead to natural recovery. In Northern
Ireland (NI) both reproduction and habitat are compromised and sufficient
improvement is unlikely to occur before the predicted date of extinction.4
Research by Roberts and researcher Jane Preston on captive breeding of
pearl mussels was initiated in 1995, in collaboration with Alan Keys
(Ballinderry Fish Hatchery)3. Captive breeding is one of the
key approaches to the restoration of endangered species, often seen as the
method of last resort. Roberts and co-workers demonstrated that large
numbers of young mussels (3,600 in 1999; 19,000 in 2000) could be
successfully propagated from a relatively small broodstock under
semi-natural conditions3. The system involves infecting trout
with mussel larvae, so that larval mussels can complete the parasitic
stage of their life cycle in the hatchery, with less than 1% host fish
mortality. This pioneering method for cultivation of pearl mussels
represents a significant breakthrough in the conservation of this species,
intermediate between the release of infected fish into rivers and the
intensive cultivation systems developed in continental Europe and the USA
for other species of pearl mussels3. Genetic research (Roberts
and geneticist Jim Provan with their research groups) in 2007-10 found
differences between captive-bred juveniles, their parent broodstock, and
mussels from the source river, indicating a loss of genetic variability
probably due to founder effects6. This issue has been addressed
by introducing new individuals to adjust the composition of the
broodstock. Habitat suitability modelling (Roberts with ecologist Neil
Reid) provided a means by which to select release sites for further
reintroductions5 where captive-bred mussels were tagged with
Passive Integrated Transponders (PIT tags) to follow their survival.
References to the research
1) Beasley C.R., Roberts D. & Mackie T.G. (1998). Does the freshwater
pearl mussel Margaritifera margaritifera L., face extinction in
Northern Ireland? Aquatic Conservation: Marine and Freshwater
Ecosystems 8: 265-272.
2) *Beasley C.R. & Roberts D. (1999). Towards a strategy for
the conservation of the freshwater pearl mussel Margaritifera
margaritifera in County Donegal, Ireland. Biological
Conservation 89: 275-284.)
3) Preston S.J., Keys A. & Roberts D. (2007). Culturing freshwater
pearl mussel Margaritifera margaritifera: a breakthrough in the
conservation of an endangered species. Aquatic Conservation: Marine
and Freshwater Ecosystems 17: 539-549.
4) *Wilson C.D. & Roberts D. (2011). Modelling distributional trends
to inform conservation strategies for an endangered species. Diversity
and Distributions 17: 182-189.
5) *Wilson C.D., Roberts D. & Reid N. (2011). Applying species
distribution modelling to identify areas of high conservation value for
endangered species: A case study using Margaritifera margaritifera
(L.). Biological Conservation 144: 821-829.
6) Wilson C.D., Beatty G.E., Bradley C.R., Clarke H.C., Preston S.J.,
Roberts D. & Provan, J. (2012). The importance of population genetic
information in formulating ex situ conservation strategies for the
freshwater pearl mussel (Margaritifera margaritifera L.) in
Northern Ireland.
Animal Conservation 15: 593-602.
*References that best indicate the quality of the underpinning research
Details of the impact
Our impact on legislation, designations, policy and practice: The
incorporation of our research outputs (Sections 2, 3) into policy
development and captive breeding of the critically endangered (IUCN Red
List) freshwater pearl mussel has benefitted this species and its habitat
locally, nationally and internationally. In Europe, Special Areas of
Conservation (SACs) are the legal instrument enforcing protection under
the Habitats Directive, with a statutory requirement for regular
monitoring. Legal protection ensures a direct link between policy and
practice as it addresses issues that affect this species, such as
over-fishing and habitat deterioration.
Northern Ireland: Our research1,2 is cited, with
detailed results and ongoing and future activities, in the Northern
Ireland Environment Agency (NIEA)'s current Margaritifera
margaritifera Species Action Plan (SAP).S1 This
undertook to establish appropriate culturing programmes for the
enhancement of populations in suitable rivers by 2010, and re-establish
one extinct population by 2015. Because natural populations are dominated
by ageing individuals, captive breeding is required to produce young
mussels for restocking rivers. In 1995, the research collaboration between
QUB and Ballinderry Fish Hatchery (funded through Department of the
Environment Northern Ireland and WWF)3 started using
techniques differing from the initial mussel cultivation attempts in the
Czech Republic and Germany. Elsewhere in Europe, and in similar programmes
for endangered freshwater mussels in the USA, mussels are harvested from
host fish and grown in cages.S8 Our method, developed
with the Ballinderry Fish Hatchery, releases fish carrying larval mussels
into semi-natural containers to grow on, which is less labour intensive,
hence cheaper and more practicable. S6
350 nine-year old captive-bred mussels were released between 2008 and
2009 into natural sediments in their natal Ballinderry River where the
remnant population consists of <900 mussels. Each mussel was
individually PIT tagged and survival rates after three years were very
high (99% at some sites). This compares very favourably with survival
rates elsewhere of 0-20% after two years, summarized in Table 2 of McIvor
and Aldridge's 2008 report for CCW.S7 In 2009, the
Ballinderry Fish Hatchery Trust won an Association of Rivers Trusts
Contribution to Science Award for setting up Europe's first successful
freshwater pearl mussel breeding project, with our scientific input. We
achieved the NIEA's SAP target of developing an appropriate culturing
programme by 2010, which resulted in a policy document for ex situ
conservation and reintroduction of pearl mussels adapted from the IUCN
Guidelines for ReintroductionsS2. Our habitat
suitability modelling6 has identified sites for reintroduction
experiments, important progress towards the SAP target of reintroducing an
extinct population by 2015.
In 2013, 240 captive-bred juveniles 4-21 mm long, all PIT tagged, have
been released to sanctuary sites in the natal river, and an equal number
will be placed in specially designed `mussel-silos' that ensure constant
water flow. Our research has contributed to the establishment of sanctuary
sites to which mussels from remnant, functionally extinct populations in
the same river are moved with juveniles from the captive breeding
programme — a novel approach in Europe. Sanctuary populations are used for
further captive breeding and release. The Mussel Rescue ProjectS6
runs from 2012-15, with UK Lottery funding (£450k) awarded to Ballinderry
Rivers Trust and scientific input from Roberts, Reid, O'Connor and PhD
student Rebecca Kyle. It includes catchment-level restoration and
contributes to the strategic River Basin Management Plan for the Neagh
Bann, as part of the delivery of the EU Water Framework Directive
(2000/60/EC).S6
Great Britain: The UK Biodiversity Action Plan (BAP) for Margaritifera
margaritiferaS3 cites our work1 to
provide background information on selection criteria for Special Areas of
Conservation (SACs). JNCC's policy of selecting SACsS4
for Margaritifera further cites our research on population sizes
and age structure1, noting that increasing rarity in mainland
Europe gives extra significance to UK populations3.
Europe: Our research findings on the rapid and drastic decline of
pearl mussels in north-west Ireland2, due to poor water quality
and high siltation from land drainage and run-off from agriculture and
forestry, directly informed Article 11 surveillance under the EC Habitats
Directive in the Republic of IrelandS5. Because our
captive breeding program1 is amongst the most successful in
reviews of captive breeding techniquesS7-S8 it is now
being emulated in AustriaS10, where the pearl mussel is
one of the most threatened species, with no natural reproduction.
Following the complete failure of all previous attempts at assisted
breeding of mussels in the River Waldaist, an 18-year action plan is
underway, including use of our captive-breeding techniques and fish
hatcheriesS9. This began in 2009, funded by the Office
of the State Government of Upper Austria.
Sources to corroborate the impact
S1) NIEA (2005) Northern Ireland Species Action Plan: Freshwater pearl
mussel Margaritifera margaritifera. http://www.doeni.gov.uk/niea/fwpearlmussel_pdf.pdf
S2) Wilson C.D., Keys A., Horton M., Moorkens E., Roberts D. & Reid
N. 2012. Protocols for the ex situ conservation and reintroduction of
the freshwater pearl mussel Margaritifera margaritifera in
Northern Ireland. Prepared for Northern Ireland Environment Agency
Research and Development Series No. 12/09. Belfast.
S3) JNCC (2010) UK Priority Species data collation Margaritifera
margaritifera
http://jncc.defra.gov.uk/_speciespages/437.pdf
S4) http://jncc.defra.gov.uk/protectedsites/sacselection/species.asp?featureintcode=s1029
S5) NPWS (2012) Report on the main results of the surveillance under
article 11 for annex II, IV and V species (Annex B).
<http://npws.ie/publications/archive/1029_Freshwater_Pearl_Mussel_assessment.pdf
>
S6) The Ballinderry Freshwater Pearl Mussel Rescue Project Conservation
Management Plan [2012-2015]
S7) McIvor A. & Aldridge D. 2008. The cultivation of the freshwater
pearl mussel, Margaritifera margaritifera. CCW Contract Science
Report No: 849, Countryside Council for Wales/Environment Agency, Bangor.
S8) Thomas G.R., Taylor J. & Garcia de Leaniz C., 2010. Captive
breeding of the endangered freshwater pearl mussel Margaritifera
margaritifera. Endangered Species Research. 12, 1-9.
S9) Csar D., Scheder C. & Gumpinger C. 2012. The freshwater pearl
mussel in Austria — current status and prospects for the future. In:
Henrikson, L., Arvidsson, B. and Osterling, M. (eds.) Aquatic conservation
with focus on Margaritifera margaritifera. Proceedings of the
International Conference in Sundsvall, Sweden, 12-14 August, 2009.
Karlstad University Studies 2012:40.
http://www.wwf.se/source.php/1509189/Proceedings%20FPM%20Conference%20in%20Sweden.pdf
S10) Supporting letter from Museo Nacional de Ciencias Naturales
(MNCN-CSIC)