What is LIFE PINNACARE
LIFE PINNACARE is a European project devoted to the protection and restoration of the fan mussel Pinna nobilis populations in the Mediterranean Sea.
It is has been conducted with the contribution of the LIFE programme, the European Union’s financial instrument supporting environmental, nature conservation and climate action projects.
The main objective of LIFE PINNACARE is preventing the extinction of Pinna nobilis at the short-medium term, through public awareness and collaboration, gathering existing information on the remaining populations and developing active recovery actions.
Pinna nobilis background
The case
The fan mussel Pinna nobilis (Linnaeus, 1758), an endemic and protected bivalve of the Mediterranean Sea, is affected by a Mass Mortality Event (MME) provoked by the parasitic protozoan Haplosporidium pinnae started in 2016 in Spanish waters. The populations of Pinna nobilis in the open sea have almost completely disappeared from the Mediterranean coasts, with a mortality rate close to 100%. Countries such as France, Italy, Greece, Cyprus, Montenegro and Croatia have already reported the impact of the MME. The spread of the disease is so fast and its consequences so hard that the extinction of the species has been considered plausible. A compilation of recommended actions has been recently suggested (IUCN, 2019).
Remnant populations denoted as open circles. From Katsanevakis et al 2021
From the legal side, the fan mussel has been labeled as 'En Peligro de Extinción' by the Spanish 'Catálogo Nacional de Especies Amenazadas (Orden TEC/596/2019)'. Given the fast spread of the disease, and the extreme mortality rates observed, the IUCN has recently included P. nobilis in its red list of species endangered with extinction worldwide.

The disease
The disease of the fan mussel is caused by a recently discovered parasitic protozoan, Haplosporidium pinnae, to our knowledge affecting only P. nobilis. Other bacterial pathogens have also been observed in weak fan mussels, probably acting as opportunistic agents, such as Mycobacterium sp or infecting fan mussels reared in captivity, such as Vibrio shiloi. Altogether, these opportunistic agents form a conserved consortium of microorganisms cooperating to induce pathogenesis.
H. pinnae produces a systemic infection of the connective tissues, where free uninucleated stages (1.8- 4.6 μm maximum length) and plasmodia can be observed, while spore formation takes place in the digestive tubules epithelium, thus disrupting the digestive function and, finally, causing the death of the individual. . In the case of H. pinnae, although the possibility of an intermediate host cannot be discarded, healthy individuals confined with sick individuals appear to get infected directly, which supports direct transmission. The combined effect of sporulation on the digestive gland with direct transmission that this parasite seems to possess would explain its unprecedented lethality.
Actual situation
SPAIN
Concerning survival of P. nobilis at the wild, after different waves of the MME, a search for survivors from 2018 in Spanish coasts has produced a very discouraging result: No more than 10 living individuals have been observed in the wild to date, including sightings in the Columbretes Islands, the Balearic Islands, and Cap de Creus. It is noteworthy that two small Spanish fan mussel populations remain not severely impacted by the MME, but they are both located in paralic environments (Delta del Ebro and Mar Menor lagoon). The reason why these populations remain at least partially protected has been associated with particular salinity conditions, either lower or higher, respectively than the open sea. In the Alfacs Bay, there are evidences that salinity conditions below 36 confer certain tolerance against the parasite, whereas ranges below 30-32 in the Fangar Bay, appear to prevent the infection.
Concerning the second population (Mar Menor lagoon), the remaining fan mussels that had survived the environmental collapse in 2016, before the arrival of the disease, suffered a severe flood episode in September 2019. The total of specimens that remain alive is unknown, but at least several docens have been located in the least affected areas.
FRANCE
The mass mortality of fan mussels along the French coasts first appeared in the western coast of Corsica in autumn 2017. Populations of P. nobilis remain alive in coastal lagoons both in Occitania (Leucate, Thau, Fos: Rhône’s delta) and in the east coast of Corsica (Diana). In Diana a dense healthy population was observed in June 2019. In Thau lagoon, well-known populations have been monitored for several years.
ITALY
In Italy, small surviving populations of Pinna nobilis persist in the lagoon systems of Venice and Capo Peloro (Messina), where targeted conservation strategies are being applied to ensure their continued survival. In the Italian coast, the first description of MMEs in 2017 was reported in the Tyrrhenian Sea, in the region of Campania, in the islands of Ischia and Procida, and in the Sicilian coasts of Messina. By March 2018, the populations of Sorrento and from the islands totally disappeared. Few young individuals were observed in the south of the coast (Cilento) in 2019 and in the internal marine lakes of Phlegrean area (north of Naples). Mortality was also reported in many other Italian regions, like Sardinia and Tuscany. In Sardinia, in Oristano and in Asinara Island (north-west of Sardinia) mortality was reported since 2018, and currently no live individuals are present in these areas.
In the western Ionian Sea (, the first evidence of mortality of P. nobilis (40% of the individuals) was reported in summer 2017. Later, in the early summer 2018, the western Ionian Sea P. nobilis populations suffered very high mortalities, with up to 100% mortality in 3 months.
GREECE
The status of P. nobilis in the eastern Ionian Sea was assessed, based on data collected at 69 sites in 2019. Mortality rates exceeded 80% by August 2019, and kept increasing at that time. In autumn 2019, in all sites surveyed there was almost no live individual. The only locality, where mortality rates were low (40%) was the National Marine Park of Zakynthos, surveyed in August 2019. However, in 2020 the fan mussel population in NMPZ was largely affected, with only few live individuals left, mostly juveniles. Nevertheless, the eastern Ionian Sea remains under-sampled.
In a broader context, the mortality has reached practically all the Mediterranean basin in the open sea, and some sanctuary areas host P. nobilis population in particular conditions. Survivors/resistant individuals are few and far between but the monitoring and protection of those individuals is extremely important for the conservation of the species.

Project title
Protection and restoration of Pinna nobilis populations as a response to the catastrophic pandemic started in 2016
Duration
Start date: 1 October 2021
End date: 31 December 2024
Acronym and reference
LIFE PINNARCA
LIFE20 NAT/ES/001265
Cost
Total budget for the project: 2.249.332€
European financial contribution: 1.347.894€

Our Goals
Prevent the extinction of Pinna nobilis
in the Mediterranean by protecting surviving individuals and resistant populations.
Actions
Discover the purpose of the actions and explore each action's deliverables on the Documents section
A
Preparatory actions
A1) Selection and assessment of priority conservation sites
Identification and ecological characterization of optimal sites for conservation, reintroduction, and long-term protection of Pinna nobilis.
A2) Biosecurity planning and risk assessment
Development of site-specific biosecurity protocols to prevent disease transmission during monitoring, translocation, and ex situ activities.
C
Conservation Actions
C1) Installation of larval collectors
Deployment of collectors to assess natural recruitment and support ex situ reproduction programs.
C2) Exploration and management of natural populations
Surveying and mapping surviving and resistant individuals in coastal lagoons, marine protected areas, and open-sea sites.
C3) Optimization of ex situ maintenance and reproduction protocols
Improvement of husbandry techniques, controlled breeding, and maintenance of healthy individuals in tank systems.
C4) Genomic determination and molecular analysis
Genetic and genomic analyses to identify resistant individuals and guide conservation strategies.
C5) Disease diagnostics and treatment assays
Health assessments, pathogen screening, and experimental treatment protocols to mitigate disease impacts.
C6) Environmental improvement in sanctuary areas
Implementation of targeted habitat restoration and environmental enhancement measures in priority sites.
D
Monitoring project actions
D1) Follow-up of juvenile individuals
Monitoring growth, survival, and adaptation of juveniles produced ex situ or recruited naturally.
D2) Follow-up of resistant and translocated individuals
Long-term tracking of resistant specimens and relocated individuals to evaluate conservation success.
D3) Monitoring of environmental improvement measures
Assessment of habitat restoration effectiveness and environmental parameter stability.
D4) Monitoring and evaluation of project impact
Ecological data collection and performance indicators to measure the effectiveness of conservation actions.
D5) Development of socioeconomic impact studies
Evaluation of the social and economic benefits associated with species conservation and habitat restoration.
E
Public awareness and dissemination of results
E1) Public awareness, stakeholder engagement and citizen science
Dissemination activities, educational materials, workshops, and active involvement of divers, local communities, and institutions.
E2) Transferability, sustainability and replication of project results
Development of guidelines, best practices, and strategic plans to ensure long-term sustainability and replication across the Mediterranean.
F
Project Management
F1) General project coordination
Administrative, financial, and technical coordination of the consortium.
F2) Supervision and quality control
Continuous monitoring of project implementation, ensuring compliance with LIFE Programme regulations.
F3) After-LIFE Sustainability Plan
Strategic planning to ensure continuity of conservation actions beyond the project’s duration.

