Invasion History
First Non-native North American Tidal Record: 1986First Non-native West Coast Tidal Record:
First Non-native East/Gulf Coast Tidal Record: 1986
General Invasion History:
Mytella charruana is native to the tropical Western Atlantic from Colon, Panama (Ruiz et al., unpublished data) to Argentina (Lee 2001; Boudreaux and Walter 2006; Gillis et al. 2009). This mussel is also reportedly present in the tropical East Pacific, from Sonora, California to Ecuador, and the Galapagos Islands. However, Ecuadoran specimens were genetically distinct from Colombian (Caribbean Sea) or southeast US specimens, and showed no genetic overlap at the examined DNA sites (Gillis et al. 2009). Pacific M. charruana could represent a distinct cryptic species from the Atlantic form.
North American Invasion History:
Invasion History on the East Coast:
In 1986, a heavy infestation of small mussels, later identified as Mytella charruana clogged the intakes of the Blount Island electrical generating plant in Jacksonville, Florida (FL). The mussels disappeared in the winter of 1987, but reappeared in the St. Johns estuary in 2006 (Lee 2008). In 2006 and 2007, they were found in small numbers, and in 2008, they again clogged the Blount Island Power plant (Lee 2008). It is not clear whether small, undetected populations persisted after the die-off, or whether the initial population was completely extirpated, and one or more subsequent invasions occurred. Genetic studies have found high genetic diversity, exceeding that in native Colombian populations (Gillis et al. 2009). In 2004, Mytella charruana was discovered in Mosquito Lagoon, FL part of the Indian River Lagoon system (Boudreau and Walters 2006). After 2006, they were found along the coast north to South Carolina, and appear to be established from central Florida to the central Georgia coast (Lee 2008; USGS Nonindigenous Species Program 2008; Gillis et al. 2009; Spinuzzi et al. 2012). Sporadic records have occurred north to Charleston, South Carolina (Pam Fuller, USGS, personal communication). However, severe winter weather in 2010 and 2011 has affected the abundance of other warm-water invaders in the region (Perna viridis, Green Mussel; Petrolisthes armatus, Green Porcelain Crab; Canning-Clode and Fowler, unpublished data), and has also reduced the range or abundance of M. charruana (Spinuzzi et al. 2012).
Invasion History Elsewhere in the World:
In 2014, Mytella charruana was genetically identified in the port of Manila, Philippines, and found to be established in Manila Bay (Vallejo et al. 2017).
Description
Mytella strigata is small, thin-shelled, and lacks exterior ribs on its shell surface. On the interior of the shell the byssal retractor scar is nearly circular, and located further from the back than the more elongated, irregular scar in Mytilus edulis. The outside of the shell is light-green to black, and may be uniform or banded in a crisscross pattern. The internal surface of the shell is purple. The largest reported specimen of M. strigata is 48.7 mm, but a more typical size is 20-25 mm. (Description from: Lee 2001; Boudreaux and Walters 2006; Stenyakina et al. 2010)
Ecuadoran populations were genetically distinct, and did not overlap with Colombian (Caribbean) or introduced Florida and Georgia populations. Specimens of M. strigata were also genetically distinct from specimens of Mytella guyanensis from Brazil (Gillis et al. 2009).
This mussel was widely known under the name M. charruensis (d'Orbigny, 1846). Lim et al. (2018) and other recent authors (Sampanich and Wells 2019) and Tay et al. (2019) use the name Mytella strigata for this mussel, based on a detailed examination of 19th century publication dates (Lim et al. 2018). The World Registry of Marine Species now uses uses M. charruana (Appeltans et al. 2019).
Taxonomy
Taxonomic Tree
Kingdom: | Animalia | |
Phylum: | Mollusca | |
Class: | Bivalvia | |
Subclass: | Pteriomorphia | |
Order: | Mytiloida | |
Family: | Mytilidae | |
Genus: | Mytella | |
Species: | strigata |
Synonyms
Mytilus charruanus (d'Orbigny, 1842)
Modiola strigata (Reeve, 1857)
Mytilus falcatus (d'Orbigny, 1846)
Mytilus sinuatus (Reeve, 1857)
Mytella charruana ((d'Orbigny), 1842)
Potentially Misidentified Species
None
Geukensia demissa
None
Mytella guyanensis
A closely related species, also known from the Caribbean-Brazil and tropical East Pacific (Mexico-Peru) (Gillis et al. 2009).
Mytilus edulis
None
Ecology
General:
Mytella strigata maintains separate sexes under conditions of steady food supply, but starvation results in a change of many individuals from female to male (Stenyakina et al. 2010). Eggs and sperm are released into the water. Development is planktotrophic with eggs developing into planktotrophic larvae and veligers, settling after about 14days at 29 C (Tan et al. 2018).
Mytella strigata is especially common in estuarine and lagoon environments. In Brazil, it is known from mangrove, mudflat, and rocky habitats (de Oliveira et al. 2005). In its introduced range, in the southeast US, it has been found on oyster beds, disarticulated shells, wood, roots, etc., but adult mussels were more common on artificial substrates, such as docks and power plants (Gilg et al. 2010; Lee 2001-2011). This mussel tolerates a wide range of salinities from 2 to 40 PSU (Yuan et al. 2010), but tolerance of low temperatures is limited. N the St. Johns River estuary, Florida, M. charruana was found at sites with average salinities ranging from 13 to 33 PSU, and highest densities at a mean salinity of 21 PSU). The upper temperature limit is at least 31?C, and likely to be higher (Brodsky et al. 2009- http://www.sicb.org/meetings/2009/schedule/abstractdetails.php3?id=413). I
Food:
Phytoplankton, detritus
Trophic Status:
Suspension Feeder
SusFedHabitats
General Habitat | Coarse Woody Debris | None |
General Habitat | Mangroves | None |
General Habitat | Marinas & Docks | None |
General Habitat | Rocky | None |
General Habitat | Unstructured Bottom | None |
Salinity Range | Mesohaline | 5-18 PSU |
Salinity Range | Polyhaline | 18-30 PSU |
Salinity Range | Euhaline | 30-40 PSU |
Tidal Range | Subtidal | None |
Tidal Range | Low Intertidal | None |
Vertical Habitat | Epibenthic | None |
Life History
Tolerances and Life History Parameters
None | 4.9 | Maximum size at maturity (12.5 mm, Stenyakina et al. 2010) |
Minimum Temperature (ºC) | 6 | Experimental data, stepwise transfers (Brodsky et al. 2009) http://www.sicb.org/meetings/2009/schedule/abstractdetails.php3?id=413 |
Maximum Temperature (ºC) | 31 | Experimental data, stepwise transfers (Brodsky et al. 2009) http://www.sicb.org/meetings/2009/schedule/abstractdetails.php3?id=413 |
Minimum Salinity (‰) | 2 | Experimental data, Yuan et al. 2010 |
Maximum Salinity (‰) | 40 | Experimental data, Yuan et al. 2010 |
Maximum Duration | 14 | Larval duration, 29 C (Tay et al. 2018) |
Minimum Length (mm) | 4.9 | Stenyakina et al. 2010 |
Maximum Length (mm) | 12.5 | Minimum size at maturity (12.5 mm, Stenyakina et al. 2010) |
Broad Temperature Range | None | Warm temperate-Tropical |
Broad Salinity Range | None | Mesohaline-Euhaline |
General Impacts
In its introduced range in the southeastern US, Mytella charruana has shown a preference for settlement on natural substrates, such as disarticulated shells, wood, roots, etc., but survival was much greater on artificial substrates, such as docks and power plants (Gilg et al. 2010; Lee 2001-2011). Consequently, strong ecological impacts have not been reported in natural environments. This mussel is a local food resource in Brazil (de Oliveira et al. 2005), but is too small and rare to be utilized in the US.
In Thailand, extensive invasion by Mytilopsis sallei and Mytlella strigata (Charru Mussel) has coiverted soft-bottom lagoon communities to hard-bottom systems, resulting in the appearance and spread of some species requiring hard substrate, and the disappearance of others. However, overall changes in species richness were not seen (Wangkulangkul et al. 2022).
Economic Impacts
Industry- Heavy settlements of M. charruana in 1986 clogged the intakes of the Blount Island electrical generating plant in Jacksonville, Florida. The mussels disappeared in the winter of 1987, but reappeared in the St. Johns estuary in 2006 (Lee 2008), and in 2008 they again clogged the Blount Island Power plant (Lee 2008).
Regional Impacts
S180 | St. Johns River | Economic Impact | Industry | ||
In 1986, a heavy infestation of Mytella strigata clogged the intakes of the Blount Island electrical generating plant. The mussels disappeared in the winter of 1987, and did not reappear in the St. Johns estuary until 2006 (Lee 2008). In 2006 and 2007, they were found in small numbers, but in 2008, they again clogged the Blount Island Power plant (Lee 2008). | |||||
CAR-VII | Cape Hatteras to Mid-East Florida | Economic Impact | Industry | ||
In 1986, a heavy infestation of Mytella strigata clogged the intakes of the Blount Island electrical generating plant, in Jacksonville, Florida. The mussels disappeared in the winter of 1987, and did not reappear in the St. Johns estuary until 2006 (Lee 2008). In 2006 and 2007, they were found in small numbers, but in 2008, they again clogged the Blount Island Power plant (Lee 2008). | |||||
S190 | Indian River | Ecological Impact | Competition | ||
In experiments in Mosquito Lagoon, Florida, Mytella charruana, on fouling plates, did not affect the settlement of larvae of Eastern Oyster (Crassostrea virginica), but did reduce growth of oyster spat (Yuan et al. 2016). Feeding experiments show an overlap between M. charruana and the native oysters, and also a higher clearance rate for the mussels (Galimany et al. 2016). | |||||
CAR-I | Northern Yucatan, Gulf of Mexico, Florida Straits, to Middle Eastern Florida | Ecological Impact | Competition | ||
In experiments in Mosquito Lagoon, Florida, Mytella strigata, on fouling plates, did not affect the settlement of larvae of Eastern Oyster (Crassostrea virginica), but did reduce growth of oyster spat (Yuan et al. 2016). Feeding experiments show an overlap between M. strigataa and the native oysters, and also a higher clearance rate for the mussels (Galimany et al. 2016). | |||||
EAS-I | None | Economic Impact | Fisheries | ||
Negative impacts on commerical mussel culture of Perna perna, but a resource for local, informal shellfish gathering and aquaculturie (Fuertes et al. 2021). | |||||
EAS-I | None | Ecological Impact | Habitat Change | ||
In Thailand, extensive invasion by Mytilopsis sallei and Mytlella strigata (Charru Mussel) has coiverted soft-bottom lagoon communities to hard-bottom systems, resulting in the appearance and spread of some species requiring hard substrate, and the disappearance of others. However, overall changes in species richness were not seen (Wangkulangkul et al. 2022) |
|||||
FL | Florida | Ecological Impact | Competition | ||
In experiments in Mosquito Lagoon, Florida, Mytella charruana, on fouling plates, did not affect the settlement of larvae of Eastern Oyster (Crassostrea virginica), but did reduce growth of oyster spat (Yuan et al. 2016). Feeding experiments show an overlap between M. charruana and the native oysters, and also a higher clearance rate for the mussels (Galimany et al. 2016). | |||||
FL | Florida | Economic Impact | Industry | ||
In 1986, a heavy infestation of Mytella strigata clogged the intakes of the Blount Island electrical generating plant. The mussels disappeared in the winter of 1987, and did not reappear in the St. Johns estuary until 2006 (Lee 2008). In 2006 and 2007, they were found in small numbers, but in 2008, they again clogged the Blount Island Power plant (Lee 2008). |
Regional Distribution Map
Bioregion | Region Name | Year | Invasion Status | Population Status |
---|---|---|---|---|
SA-IV | None | 0 | Native | Established |
SA-III | None | 0 | Native | Established |
SA-II | None | 0 | Native | Established |
CAR-III | None | 0 | Native | Established |
CAR-VI | None | 0 | Native | Established |
CAR-VII | Cape Hatteras to Mid-East Florida | 1986 | Non-native | Established |
CAR-I | Northern Yucatan, Gulf of Mexico, Florida Straits, to Middle Eastern Florida | 2004 | Non-native | Established |
S180 | St. Johns River | 1986 | Non-native | Established |
S190 | Indian River | 2004 | Non-native | Established |
S140 | St. Catherines/Sapelo Sounds | 2006 | Non-native | Established |
S090 | Stono/North Edisto Rivers | 2008 | Non-native | Unknown |
S183 | _CDA_S183 (Daytona-St. Augustine) | 2006 | Non-native | Established |
S170 | St. Marys River/Cumberland Sound | 2007 | Non-native | Established |
S110 | Broad River | 2009 | Non-native | Unknown |
SEP-I | None | 0 | Crypogenic | Established |
SEP-Z | None | 0 | Crypogenic | Established |
NEP-VII | None | 0 | Crypogenic | Established |
NEP-VIII | None | 0 | Crypogenic | Established |
NEP-IX | None | 0 | Crypogenic | Established |
SEP-H | None | 0 | Crypogenic | Established |
S160 | St. Andrew/St. Simons Sounds | 2007 | Non-native | Established |
S150 | Altamaha River | 2009 | Non-native | Established |
S120 | Savannah River | 2008 | Non-native | Established |
S080 | Charleston Harbor | 2016 | Non-native | Unknown |
S070 | North/South Santee Rivers | 2016 | Non-native | Unknown |
EAS-I | None | 2014 | Non-native | Established |
PAN_CAR | Panama Caribbean Coast | 0 | Native | Established |
EAS-VI | None | 2016 | Non-native | Established |
CIO-I | None | 2019 | Non-native | Established |
NWP-3a | None | 2019 | Non-native | Established |
NWP-2 | None | 2020 | Non-native | Established |
Occurrence Map
OCC_ID | Author | Year | Date | Locality | Status | Latitude | Longitude |
---|
References
Ames, Cheryl and 15 authors (2020) Cassiosomes are stinging-cell structures in the mucus of the upside-down jellyfish Cassiopea xamachana, Communications Biology 3.67: Published onlinhttps://doi.org/10.1038/s42003-020-0777-8
Appeltans, W. et al. 2011-2015 World Registry of Marine Species. <missing URL>
Berquist, Patricia R. (1970) The Marine Fauna of New Zealand: Porifera, Demospongiae, Part 2 , New Zealand Oceanographic Institute Monographs 51: 1-87
Boudreaux, Michelle L.; Stiner, Jennifer L.; Walters, Linda J. (2006) Biodiversity of sessile and motile macrofauna on intertidal oyster reefs in Mosquito Lagoon, Florida., Journal of Shellfish Research 25(3): 1079-1089
Boudreaux, Michelle L.; Walters, Linda (2006) Mytella charruana (Bivalvia: Mytilidae): a new invasive bivalve in Mosquito Lagoon, FL, Nautilus 120(1): 34-36
Calazans, Savio H.; Walters, Linda J.;; Fernandes, Flavio C. , Ferreira, Carlos E. L. ; Hoffman, Eric; A. (2017) Genetic structure provides insights into the geographic origins and temporal change in the invasive charru mussel (Sururu) in the southeastern United States, PLOS ONE 12(7): e0180619
de Oliveira, Miguel E.G.C.; Russo, Claudia A.M.; Lazoski, Cristiano Vianna, Paulo Roberto F.G.; Solé-Cava, Antonio M. (2005) Genetic variation and population structure of two species of neo-tropical mud-mussels (Mytella spp), Genetics and Molecular Research 4(2): 197-202
de Souza, Thainara Oliveira and 6 authors (2015) Population structure and identification of two matrilinear and one patrilinear mitochondrial lineages in the mussel Mytella charruana, Estuarine, Coastal and Shelf Science 156: 165-174
Fisheries and Oceans Canada 2018 Perkinsus marinus ("Dermo" Disease) of Oysters. https://www.dfo-mpo.gc.ca/science/aah-saa/diseases-maladies/pmdoy-eng.html
Gabay, Yasmin; Weis, Virginia M.; Davy, Simon K (2018) Symbiont Identity Influences Patterns of Symbiosis Establishment, Host Growth, and Asexual Reproduction in a Model Cnidarian-Dinoflagellate Symbiosis, Biological Bulletin 234: 1-10
https://doi.org/10.1086/696365
Gilg, Matthew R. and 5 authors (2010) Recruitment preferences of non-native mussels: Interaction between marine invasions and land-use changes, Journal of Molluscan Studies 76: 333-339
Gillis, Nancy K.; Walters, Linda J.; Fernandes, Flavio C.; Hoffman, Eric A. (2009) Higher genetic diversity in introduced than in native populations of the mussel Mytella charruana: evidence of population admixture at introduction sites, Diversity and Distributions 15: 784-795
Herrera, Marcela; Klein, Shannon G.;Schmidt-Roach, Sebastian; Campana, Sara; Cziesielski Maha J.; Chen, Jit Ern; Duarte Carlos M.; Aranda, Manuel (2020) Unfamiliar partnerships limit cnidarian holobiont acclimation to warming, Global Change Biology 26(26): 5539–5553
https://doi.org/10.1111/gcb.15263
Joyce, Patrick W.S.; Lee, Shing Yip; Falkenberg, Laura J. (2023) First record of the invasive alien mussel Mytella strigata (Hanley, 1843) in Hong Kong, BioInvasions Records 12: Published online
Lee, Harry 2001-2015 Harry Lee's Florida Mollusca Checklists. <missing URL>
Lodeiros, César; Hernández-Reyes, Dailos; Salazar, José Miguel; Rey-Méndez, Manuel; González-Henríquez, Nieves (2021) First report of the mussel Mytella strigata (Hanley, 1843) in the Venezuelan Caribbean from an invasion in a shrimp farm, Latin American Journal of Aquatic Research 49(3): 531-537
Ma. Pei-Zhen; Li, Hou-Mei; Liu, Yu-Meng; Li, Cui; Zhang, Zhen; Wang, Hai-Yan (2022) First confirmed occurrence of the invasive mussel Mytella strigata (Hanley, 1843) in Guangdong and Hainan, China, and its rapid spread in Indo-West Pacific regions, BioInvasions Records 11(4): 947–963
https://doi.org/10.3391/bir.2022.11.4.13
Madrid, Maycol; Collin, Rachel (2021) A checklist of the mollusks from the Miraflores and Pedro Miguel locks, Panama canal, panama, Technociencia 23(2): 125-150
Martaeng. Rasmus Obst, Matthias; Kuklinski, iotr (2023) Phylogeographic study using autonomous reef monitoring structures indicates fast range expansion of the invasive bryozoan Juxtacribrilina mutabilis, Hydrobiologia <missing volume>: Published online
https://doi.org/10.1007/s10750-023-05184-9
Puyana, Mónica;; Prato, Julián; Día, Juan Manuel (2012) Mytella charruana (d’Orbigny) (Mollusca: Bivalvia: Mytilidae) en aa Bahía de Cartagena, Colombia, Boletín de Investigaciones Marinas y Costeras 41(1): 213-217
Smithsonian Marine Station at Fort Pierce 2007-2022 Indian River Species Inventory. https://www.irlspecies.org/index.php
Spinuzzi, Samantha and 5 authors (2012) <missing title>, University of Central Florida, Orlando FL. Pp. unpaged
Stenyakina, A.; Walters, L. J.; Hoffmam, E. A.; Calestani, C. (2010) Food availability and sex reversal in Mytella charruana, an invasive bivalve in the southern United States., Molecular Reproduction and Development 77: 222-230
USGS Nonindigenous Aquatic Species Program 2003-2024 Nonindigenous Aquatic Species Database. https://nas.er.usgs.gov/
Uttieri, Marco and 24 authors (2023) The Distribution of Pseudodiaptomus marinus in European and Neighbouring Waters—A Rolling Review, Journal of Marine Science and Engineering 11(1238): Published online
https://doi.org/10.3390 /jmse11061238
Wangkulangkul, Kringpaka; Hayeewachi, Lutfee; Rodcharoen, Eknarin (2022) Changes in benthic macro-invertebrate assemblages in an estuary in southern Thailand after invasion by non-native bivalves Mytilopsis sallei and Mytella strigata, Plankton & Benthos Research 17(2): 137–146
doi: 10.3800/pbr.17.137
Yu, Yanan' Gao, Qi; Liu, Mengling; Li, Jingqi; Wang, Shuo; Zhang, Junlong (2023) Report on the invasive American brackish-water mussel Mytella strigata (Hanley, 1843) (Mollusca: Mytilidae) in Beibu Gulf, BioInvasions Records <missing volume>: Published online
Yuan, W. Samantha; Hoffman, Eric A.; Walters, Linda J. (2016) <missing title>, 18 <missing publisher>, <missing place>. Pp. 689-701
Yuan, Wei; Walters, Linda J.; Schneider, Kimberly R.; Hoffman, Eric A. (2010) Exploring the survival threshold: a study of salinity tolerance of the nonnative mussel Mytella charruana, Journal of Shellfish Research 29(2): 415-422