Description
This species has both an asexual hydroid and a sexual medusa stage, both forms have been collected from Chesapeake Bay (Calder 1971). Calder's specimens were identified by W. J. Rees, British Museum, and P. L. Kramp, Zoological Museum; Copenhagen.
Order - Naumov (1969) and earlier authors placed the Moerisiidae in the Limnomedusae, but Rees (1957) and others (Mills and Sommer 1995) put this family among the Anthomedusae.
Potentially Misidentified Species.- Moerisia pallasi is very similar to M. lyonsi, native to the Black Sea (Naumov 1969).
Taxonomy
Kingdom | Phylum | Class | Order | Family | Genus |
---|---|---|---|---|---|
Animalia | Cnidaria | Hydrozoa | Anthomedusae | Moerisiidae | Moerisia |
Synonyms
Invasion History
Chesapeake Bay Status
First Record | Population | Range | Introduction | Residency | Source Region | Native Region | Vectors |
---|---|---|---|---|---|---|---|
1965 | Established | Unknown | Introduced | Regular Resident | Eastern Atlantic | Eastern Atlantic | Shipping(Ballast Water,Fouling Community) |
History of Spread
The hydrozoan Moerisia lyonsi is only known from its type locality, Lake Quarun Egypt (a lagoon of the Nile Delta) and the East, Gulf and West coasts of North America (Boulenger 1908; Rees 1958; Calder and Burrell 1967; Poirier and Mulino 1977; Meek et al. 2012). Other species of Moerisia are known from the Caspian Sea, Japan, and the Mediteranean, in coastal and continental salt lakes (Calder 1971; Dumont 1994). An unidentified species of Moerisia has been introduced to San Francisco Bay (Mills 1999). It is possible that M. lyonsi and other named forms may represent a single, morphologically plastic species of Ponto-Caspian origin (Mills 1999).
Atlantic Coast records are listed from south to north:
Gulf of Mexico, Lake Ponchartrain - Polyps of M. lyonsi were found in the lake spillway in 1975, but disappeared during unusually low salinities (Poirier and Mulino 1977).
South Carolina- Medusae of M. lyonsi were reported as abundant in most areas of low salinity (Calder and Hester 1978). Medusae and polyps invaded an shrimp aquaculture system at Charlestown SC in 1973 (Sandifer et al. 1974).
Chesapeake Bay - M. lyonsi medusae were first collected in 1965 and hydroids in 1965-68 in low-salinity waters of the James and Pamunkey Rivers (Calder and Burrell 1967; Calder 1971). Subsequent reports of the species are sparse, but hydroids of M. lyonsi were found in settling plates from Baltimore Harbor in 1995 (Ruiz et al. unpublished). About 1992-93, M. lyonsi medusae invaded an experimental mesocosm system at the University of Maryland Horn Point Laboratory, and were also collected in the adjacent Choptank river (Purcell et al. 1999).
Delaware River and Bay- M. lyonsi was found in Delaware Bay by Dale Calder (no specific data on locality) (Calder et al. 1974).
In the San Francisco estuary, Moerisia sp. medusae and polyps were discovered in the brackish Petaluma River, a tributary of San Pablo Bay, in 1993 (Mills and Sommer 1995), and were later found in the Napa River, another San Pablo tributary. In 1997, Moerisia sp. medusae were collected in Suisun Slough (Rees and Gershwin 2000). Extensive surveys of non-indigenous hydrozoans in Suisun Marsh, and the Napa and Petaluma rivers were made by Schroeter (2008) and Wintzer et al. (2011a; 2011b). Medusae of Moerisia sp. were the most numerous of the 3 species of nonindigenous hydromedusae in Suisun Marsh, occasionally reaching densities of 100 . M-3 (Schroeter 2008l; Wintzer et al. 2008b). The San Francisco Bay hydrozoans have recently beeen found to be identical to M. lyonsi from Chesapeake Bay (Meek et al. 2012).
History References - Calder and Burrell 1967;Calder 1971;Calder and Hester 1978; Dumont 1994; Poirrier and Mulino 1977a; Purcell et al. 1999; Ruiz et al. unpublished data; Sandifer et al. 1974
Invasion Comments
Ecology
Environmental Tolerances
For Survival | For Reproduction | |||
---|---|---|---|---|
Minimum | Maximum | Minimum | Maximum | |
Temperature (ºC) | 29.0 | 10.0 | 29.0 | |
Salinity (‰) | 1.0 | 40.0 | 2.3 | 40.0 |
Oxygen | ||||
pH | ||||
Salinity Range | oligo-poly |
Age and Growth
Male | Female | |
---|---|---|
Minimum Adult Size (mm) | 2.4 | 2.4 |
Typical Adult Size (mm) | 5.4 | 5.4 |
Maximum Adult Size (mm) | 8.4 | 8.4 |
Maximum Longevity (yrs) | ||
Typical Longevity (yrs |
Reproduction
Start | Peak | End | |
---|---|---|---|
Reproductive Season | |||
Typical Number of Young Per Reproductive Event |
|||
Sexuality Mode(s) | |||
Mode(s) of Asexual Reproduction |
|||
Fertilization Type(s) | |||
More than One Reproduction Event per Year |
|||
Reproductive Startegy | |||
Egg/Seed Form |
Impacts
Economic Impacts in Chesapeake Bay
The hydrozoan Moerisia lyonsi has been a pest in closed-system aquaculture tanks used to rear Macrobrachium spp. (shrimp) larvae in SC (Sandifer et al. 1974). That occurrence and its recent spread in an experimental mesocosm system at Horn Point (Purcell et al. 1999) suggests that this species might be a pest in brackish-water aquaculture systems in the Chesapeake Bay region.
References - Sandifer et al. 1974; Purcell et al. 1999
Economic Impacts Outside of Chesapeake Bay
The hydrozoan Moerisia lyonsi is a potential pest in low-salinity aquaculture systems, and is capable of killing and/or eating decapod larvae larger than itself (Sandifer et al. 1974).
References- Sandifer et al. 1974
Ecological Impacts on Chesapeake Native Species
The hydrozoan Moerisia lyonsi appears to occur in mostly at low densities in Chesapeake Bay and has no reported impacts in natural waters. However, the medusae and polyps are easily overlooked. In an experiemental mesocosm system at Horn Point Laboratories, on the Choptank River, medusae reached sufficient densities (up to 14 . l-1) to affect copepod populations through predation. Field densities in the River reached 12.8 . l-1 in natural waters of the Choptank River, but were usually lower (Purcell et al. 1999). Predation rates of this hydrozoan are probably much smaller than those of the larger and abundant native ctenophore Mnemiopsis leidyi (Leidy's Comb-Jelly), or Chrysaora quinquecirrha (Sea-Nettle).
References- Purcell et al. 1999
Ecological Impacts on Other Chesapeake Non-Native Species
The hydrozoan Moerisia lyonsi appears to occur in low densities in Chesapeake Bay and has no reported impacts in natural waters. Impacts on other exotic biota have not been reported.
References
Calder, Dale R. (1971) Hydroids and hydromedusae of southern Chesapeake Bay., Virginia Institute of Marine Science, Special Papers in Marine Science 1: 1-125Calder, Dale R., Burrell, Victor G. (1967) Occurrence of Moerisia lyonsi (Limnomedusae, Moerisiidae) in North America, The American Midland Naturalist 78: 540-541
Calder, Dale R.; Hester, Betty S. (1978) Phylum Cnidaria., In: Zingmark, Richard G.(Eds.) An Annotated Checklist of the Biota of the Coastal Zone of South Carolina. , Columbia. Pp. 87-93
Dumont, Henri J. (1994) The distribution and ecology of the fresh- and brackish-water medusae of the world., Hydrobiologia 272: 1-12
Ma, Xingpu (2003) Effects of environmental factors on distribution and asexual reproduction of the invasive hydrozoan, Moerisia lyonsi., None , College Park MD. Pp. None
Meek, Mariah H.; Wintzer, Alpa P.; Shepherd, Nicole; May, Bernie (2012) Genetic diversity and reproductive mode in two non-native hydromedusae, Maeotias marginata and Moerisia sp., in the upper San Francisco Estuary, California, Biological Invasions 15: 199-212
Mills, C. E.; Sommer, F. (1995) Invertebrate introductions in marine habitats: two species of hydromedusae (Cnidaria) native to the Black Sea, Maeotias inexspectata and Blackfordia virginica, invade San Francisco Bay, Marine Biology 122: 279-288
Naumov, D. V. (1969) Hydroids and Hydromedusae of the U.S.S.R., , Jerusalem. Pp.
Poirrier, Michael A.; Mulino, Maureen M. (1977) Impact of the 1975 Bonnet Carré spillway opening on epifaunal invertebrates in southern Lake Pontchartrain, Journal of the Elisha Mitchell Scientific Society 93: 11-18
Purcell, J.E.; Bamstedt, U.; Bamstedt, A. (1999) Prey, feeding rates, and asexual reproduction rates of the introduced oligohaline hydrozoan Moerisia lyonsi, Marine Biology 134: 317-325
Rees, John T.; Gershwin, Lisa-Ann (2000) Non-indigenous hydromedusae in California's upper San Francisco estuary: life cycle, distribution, and potential environmental impacts., Scientia Marina 64: 73-86
Rees, W. J. (1957) The relationships of Moerisia lyonsi Boulenger and the family Moerisiidae, with captitate hydroids, Proceedings of the Zoological Society of London 130: 537-543
Sandifer, Paul A.; Smith, Theodore I. J.; Calder, Dale R. (1974) Hydrozoans as pests in closed-system aquaculture of larval decapod crustaceans, Aquaculture 4: 55-59
Schroeter, Robert E. (2008) Biology and long-term trends of alien hydromedusae and striped bass in a brackish tidal marsh in the San Francisco estuary, San Francisco Estuary and Watershed Science 13: 1-223
Wintzer, Alpa P.; Meek, Mariah H.; Moyle, Peter B. (2011c) Trophic ecology of two non-native hydrozoan medusae in the upper San Francisco estuary, Marine and Freshwater Research 62: 952-961
Wintzer, Alpa P.; Meek, Mariah H.; Moyle, Peter B.; May, Bernie (2011a) Ecological insights into the polyp stage of non-native hydrozoans in the San Francisco Estuary, Aquatic Ecology 45: 151-161