1. Introduction
The role of citizen science (CS) in invasion biology [
1,
2]
and in particular in biodiversity monitoring has been highlighted in recent literature [
3,
4].
Citizen science has existed for centuries, but the recent adoption of information and communications technology (ICT) in this field (e.g., web- or mobile application-based interfaces for citizen training and data generation) has led to a massive surge in popularity, mainly due to reduced geographic barriers to citizen participation [
5]
.
The data produced from the
cooperation of Citizen Scientists with Biological invasion experts, either directly or via information systems
such as iNaturalist [
6]
or other dedicated networks (see [
7] EASIN – European Alien Species Information Network)
has led to detecting new nonindigenous species (NIS), and document their spread, all of which help to develop policy and environmental management for Invasive Alien Species (IAS) and large-scale biodiversity conservation [
8].
Marine Citizen Science (MCS) is highly underrepresented in the citizen science literature, despite the instrumental (data-focused) and capacity-building (society-focused) benefits such projects offer for marine conservation. Nevertheless, the MCS literature has experienced continual growth since its first publications in the early 1990s [
9]
.
In the marine environment the most active group of citizen scientists are Fishers. According to Kousteni et al. [
8] with regards to fishes and molluscs, the main categories of citizen scientists at Pan-European level included school children, students, divers, naturalists, and various volunteers. Most of the CS records of molluscs were reported in NE Atlantic Ocean, mostly in the Greater North Sea. At Mediterranean level it appears that the most active CS group are fishers [
10,
11,
12]
followed by naturalists [
12]
. In Greece, 31 alien molluscan taxa were first detected by amateurs, mostly shell collectors, and SCUBA divers/photographers [
13].
The valuable contribution of amateur malacologists hereafter call SC (shell collectors) in reporting alien molluscan species in the Mediterranean has been underestimated. The aim of this work is to highlight the role of SC as the oldest and most reliable non-institutional data providers of molluscan NIS in European Seas and particularly in the Mediterranean.
2. Methodology
Molluscs were collected by Christiane Delongueville (CD) and Roland Scaillet (RS) during many trips conducted in the period 1981 to 2018 in nine countries across the Mediterranean Sea and as north as the Turkish coasts of Marmara Sea (
Table 1). The areas visited are shown in
Figure 1.
We hereby define as ”observation” any collection of a species conducted in a site at a certain time regardless of the number of specimens collected. A total of 418 observations were made, the vast majority along Mediterranean coasts with only 10 observations along the Marmara coast (Dardanelles to Bosphorus). Although many records, mostly micromolluscs, are based on empty shells they are considered as valid NIS records because their presence is confirmed by published records of living specimens in the country or other neighbouring Mediterranean countries [
13].
Most of the shells (86 %) were collected by CD and RS (hand-picked, snorkeling, scuba diving), while 14 % of records come from material provided by fishermen. All the collection details (locations, habitat, depth and status of shells) can be seen in the supplementary file. All the shells are kept in the personal collection of CD and RS.
Nomenclature was checked against WoRMS [
14].
The data on the first records and corresponding dates and sources of alien molluscs in Israel, Türkiye, Cyprus, and Greece was retrieved from the literature and the unpublished HCMR Data base administrated by Argyro Zenetos (AZ). At pan-Mediterranean scale this data was retrieved from Galanidi et al. [
15]
3. Results
In the course of a total of 418 observations, 60 alien molluscan species were identified, the most frequent of which are listed in
Table 2. The majority of species belong to the class of Gastropoda (38) while 22 species belong to Bivalvia. Among the observed specimens 54.3 % were collected alive, the rest were empty shells mostly beached or found in shell grit.
Table 3 summarizes the finding per country. Some of the records are here reported for the first time in the country or a Marine Strategy area (MSFD-Marine Strategy Framework Directive) of a country (e.g.,
Brachidontes pharaonis first record from the Levantine Sea subdivision of Greece); others are backdating species reported in the literature at a later date (e.g.,
Bulla arabica Malaquias & Reid, 2008 in South Türkiye
in 1992 backdating the 2000 record, etc.). The finding of Lioberus ligneus (Reeve, 1858) in South Türkiye in 1993, backdates all previous records and constitutes the first Mediterranean record.
The number of species found in each country is positively related to the number of observations made in each country, being more pronounced in the eastern Mediterranean (
Figure 2). However, it is not consistent with the number of visits per country. It correlates well in the eastern Mediterranean, peaking in Türkiye (15 visits, revealed 50 alien species), whereas in the western Mediterranean e.g., in France during 8 visits only 4 alien species were detected as opposed to
Cyprus (eastern Mediterranean) where 8 trips rendered 19 species (
Figure 2).
The following observations:
Chama asperella (2009, Cyprus),
Diala semistriata and
Megastomia lorioli (2002, S. Türkiye) and
Indothais lacera (1988, Malta) (
Figure 3) consitute first country /MSFD subdivision records (
Figure 3)
In addition, the finding of
Rapana venosa (Valenciennes, 1846) in 1989 consitutes the first record for S. Türkiye and that of
Chama asperella Lamarck, 1819 in 1990 from Silivri harbor the first record for the Sea of Marmara (
Figure 3).
4. Discussion
In this work we collate and report a considerable number of largely unpublished records of 60 alien molluscs in 9 countries across the Mediterranean Sea and the Sea of Marmara. Some of the observations have been previously published by CD and RS either at country level [
16] or as separate species finding [
17,
18,
19,
20,
21,
22,
23,
24,
25].
In agreement with Galanidi et al. [
15], the highest number of molluscan NIS observed in this study was found in the eastern Mediterranean. Although no pathway analysis was attempted in this work, excluding
Crepidula fornicata and
Crassostrea / Magallana sp., the vast majority of the molluscan encountered originate in the Indo-Pacific and have most likely been introduced to the eastern Mediterranean via the Suez Canal either spreading (Lessepsian immigrants) or with vessels.
The year of first detection of a NIS is essential in analyzing trends of introductions at any spatial level. The MSFD primary criterion concerning new NIS introductions states that: “The number of non-indigenous species which are newly introduced via human activity into the wild, per assessment period (6 years), measured from the reference year (2011) as reported for initial assessment under Article 8(1) of Directive 2008/56/EC, is minimised and where possible reduced to zero”. Therefore, precision in the year of first detection (a proxy of the real first introduction) is crucial in assessing the number of new introductions in an area at a given interval.
Three of our observations, coincide with findings reported in the literature at the same year (1989) from South Turkiye by SC. We refer to:
Monotygma lauta (Adams A., 1853) [
26];
Smaragdia souverbiana (Montrouzier, 1863) [
27], and
Zafra selasphora (Melvill & Standen 1901) [
28].
It is worth noting that ten of our observations, backdate the year of first detection as reported in the literature by at least a year. These are:
Afrocardium richardi (Audouin, 1826) in Türkiye 1991, backdating the 2000 record of [
29] Published by [
21];
Brachidontes pharaonis (P. Fischer, 1870) in east Rhodes (Levantine coast of Greece), 1981 backdating the 2010 record for the Levantine MSFD by [
30];
Bulla arabica Malaquias & Reid, 2008 in S. Türkiye 1992, backdating the 2000 record by [
31];
Cerithiopsis tenthrenois (Melvill, 1896) in S. Türkiye 1989, backdating the 2000 record by [
32];
Cerithiopsis tenthrenois (Melvill, 1896) in Cyprus 1984, backdating the 1985 record by [
33];
6. Dendostrea cf
folium (Linnaeus, 1758) in S. Türkiye 1989, backdating the record of 1993 by [
34];
7. Dendostrea cf
folium (Linnaeus, 1758) in Cyprus 2007, backdating the record 2008 by [
35]
Mnestia girardi (Audouin, 1826) in Cyprus 1990, backdating the 1992 record of [
36]. Published by [
37] as
Cylichnina girardi (Audouin, 1826);
Purpuradusta gracilis notata (Gill, 1858) in Cyprus 1988, backdating the 2000 record [
39];
Trochus erithreus Brocchi, 1821 in S. Türkiye, 1990, backdating the 1992 record by [
38].
Of the above, the soundest case is that of the bivalve
Brachidontes pharaonis one of the first Lessepsian invaders into the Mediterranean (x) that is widespread in the Levantine basin (eastern Mediterranean
). Yet, its presence in east Rhodes (Levantine coast of Greece) was not noted before 2010 [
30]. The present work backdates its presence in the area by 29 years and shows how a species easy to recognize can go unnoticed due to the lack of scientific effort in the area, a gap that can be filled by SC.
The following observations, even though they belong to species previously known and reported from a country, are considered first country records since the exact year of their detection had not been provided in the respective literature:
a) Chama asperella in Cyprus [
23] as
Chama aspersa Reeve, 1846; b)
Diala semistriata in Türkiye [
37] as
Diala varia Adams A., 1861;
Megastomia lorioli in Türkiye [
36] as
Odostomia lorioli (Hornung & Mermod, 1924);
Indothais lacera in Malta [
27] as
Thais lacera (Born, 1778).
Finally, the most interesting observations is that of the mytilid
Lioberus ligneus (Reeve, 1858) from S.T
ürkiye in 1993 [
40] that backdates all previous records in the Mediterranean by at least 6 years [It is worth noting that the previously reported first record of 1999 in Lebanon was reported with a lag of 14 years by Crocetta et al. [
41]]. This is an example that highlights the importance of a regular collaboration at the international level between formally trained/institutional taxonomic experts on the one hand and dedicated and experienced shell collectors on the other to fill in the gaps in our knowledge of alien Mollusca distribution.
Malacologists (SC) are the oldest citizen science group contributing to biodiversity. However, their findings are not always published. With a few exceptions they are hidden in drawers of private collections, and sometimes come to light years later if donated to natural history Museums. When it comes to alien species, surprisingly their contribution is countable. There are several publications on alien molluscs in the Mediterranean, attributed to SC, since the 1950′s when invasion biology was not yet developed as a formal/separate scientific field. In fact, approximately 37 % of alien molluscs in Israel [62 out of the 166 molluscan NIS listed by Galil et al. [
42]], has been reported by SC (notably Henk Mienis and Jacobus J. van Aartsen are the two most renowned members in the SC community). In Türkiye this figure is even higher [68 species represent 55% of the 123 alien molluscs reported by Cinar et al. [
43]]. If joint publications of SC with molluscan experts is considered, the percentage increases to 40% for Israel, 62% for Türkiye.The south Turkish, Cypriot and Greek coasts, favorite tourist destinations, have attracted the attentions of many SC, many of whom have published their findings [Germans [
39], Dutch [
29], Italians [
13,
26,
27,
28,
32,
36], Belgians [
16,
17,
18,
19,
20,
21,
22,
23,
24,
25]]. In Cyprus and Greece, the alien molluscs reported by CS reach 58 % and 40% respectively.
The iNaturalist program [
6] has been recognised as a key tool for collecting biodiversity data produced by CS in multiple nations globally. However, SC have their own means of publishing their findings. These are: dedicated journals published by their Malacological societies such as
La Conchiglia (Italy: ceased),
Triton (Israel),
Bollettino Malacologico (Italy),
Iberus (Spain),
Xenophora and
Xenophora Taxonomy (France),
Basteria (The Netherlands),
NOVAPEX (Belgium). Yet, despite all these outlets, a number of observations remains unpublished. These valuable resources should not be neglected by taxonomic experts and invasion scientists studying xenodiversity and NIS trends.
CS who are reporting their observations care about nature and their aim is to learn more about the places they visit and to protect them. SC are an important tool for monitoring the biodiversity since they are numerous, frequently present on the field, and working on a voluntary basis without requiring grants / being constrained by grants to make their observations.
Some Scientific Natural History Institutions and or Museums have recognised the importance of CS being in the field and producing interesting zoogeographical observations. They are closely working with these CS like in this case the Royal Belgian Institute of Natural Sciences (RBINS – Brussels, Belgium) but also amongst others the “Muséum national d’Histoire naturelle (MNHN – Paris, France)” and the Steinhardt Museum of Natural History, Tel Aviv, Israel.
At Mediterranean scale, it is estimated that approximately 40% of all Mediterranean NIS Mollusca [90 out of the 225 NIS [
44,
45]] have been detected by SC. Taking into account that Mollusca is the most abundant taxonomic group among NIS in the Mediterranean [
15] it is clear that collaboration of institutional experts with the malacological societies and SC will promote our knowledge on biodiversity changes and particularly on the introduction and spreading of NIS at any spatial scale.