Hypania invalida (Grube, 1860)

Common Name: Bristle worm

Synonyms and Other Names:

Freshwater bristleworm, Amphicteis invalida Grube, 1860, Hypania invalida occidentalis Ostroumouff, 1897, Phenacia oculata Schmankevitch, 1875



Copyright Info

Identification: Prostomium (anterior to mouth) contains three lobes, two glandular ridges, and two small eyespots. Gills are in two groups separated at the mid dorsum by a distance of about two gill bases; the four gills of each group have fused bases. The third body segment contains 20-35 long, weakly bent chaetae. Sixteen segments make up the thorax with notopodia containing capillary chaetae. Posterior body region contains 13 segments, also with neuropodia and uncini (short bristles). Abdomen has 15-30 uncinigerous segments, some with rudimentary notopodia containing small dorsal cirri. Thoracic uncini have one row of 5-6 teeth, while abdominal uncini have two rows of 4-6 teeth. Pygidium (terminal body region) contains 3-6 small papillae. Body color of living animal is greenish. Inhabits a self-made cylindrical tube of sand and detritus out of which it extends its feeding tentacles, which are generally no longer than the body length (Fauchald and Jumars 1979).


Size: Up to 33.5 mm in length; tube over 60 mm long and 3 mm wide


Native Range: Ponto-Caspian basin

 


This species is not currently in the Great Lakes region but may be elsewhere in the US. See the point map for details.

Ecology:  

Habitat: Hypania invalida is one of few polychaete species (<2%) able to inhabit freshwater. It lives within a muddy tube on various substrates, with a preference for fine substrates ranging from silt to gravel (Kothé 1968; Manoleli 1975; Popescu-Marinescu 1980; Rusev and Marinov 1964; Sporka 1998; Filinova et al. 2008; Norf et al. 2010, Zoric et al. 2011). It is scarce in areas with high velocity currents (Devin et al. 2006, Filinova et al. 2008, Norf et al. 2010). It may also inhabit sandy areas covered with zebra and quagga mussel beds, as H. invalida uses their shells for shelter and consumes their waste products as food (Šporka and Nagy 1998; Kurina and Seleznev 2019).  Despite this,  aggregations are not as dense in mussel beds as on soft substrates (Norf et al. 2010; Yakovleva and Yakovleva 2010). Populations can quickly build up to high densities of >10,000 individuals/m2 (46,875 ind/m2 max reported) in favorable conditions (i.e., after the building of a dam) (Popescu-Marinescu 1992; Norf et al. 2010; Pavel et al. 2021). This species also prefers to live in areas with low phosphorus concentrations (Vuckovic et al. 2021).

 

Environmental Tolerances for Hypania invalida
Environmental Parameter Value Source
Salinity 0-12ppt Mordukhai?-Boltovskoi? 1964
Temperature Range 2-25°C Mordukhai?-Boltovskoi? 1964
Depth 0-960m Zenkevich 1963
pH 8.1-8.2 Bossche et al. 2001
Oxygen 6.4–6.5 mg O2/L Bossche et al. 2001
Flow preference <0.1 m/s Norf et al. 2010

Food Web: In multiple surveys, H. invalida was observed to co-occur with the Caspian mud shrimp, Chelicorophium curvispinum (Klink and Bij de Vaate 1996; Bossche et al. 2001). It is classified as an active filter feeder and deposit feeder (Manoleli 1975), almost exclusively consuming diatoms (Manoleli et al. 1974). H. invalida has a positive relationship with mollusk populations due to having a food source from mollusk waste products (Kurina, 2023).

Life History: Hypania invalida reproduces sexually; males discharge sperm into the water column to fertilize eggs retained within the females’ dwelling tubes. Females typically carry between 50–250 eggs per clutch (Norf et al. 2010), though up to 970 eggs in a single female dwelling tube has been reported (Skal’skaya 2008). Mean egg size is 225 x 190 µm (Norf et al. 2010). Eggs are relatively protected in the mother’s dwelling tube (Schroeder and Hermans 1975). This species is iteroparous (produces multiple generations per breeding season) and females can produce new clutches every two weeks under ideal conditions with the potential for a single female to produce at least 1200 larvae in a lifetime (Norf et al. 2010). Offspring are brooded for about 2 weeks before they leave the parental dwelling tube and enter the water column. Larvae are <300µm when they colonize the sediment, reaching sexual maturity within 12 weeks after settlement. The ratio of females to males is typically 1:1, though following a population decline, females seem to become slightly more numerous than males. Additionally, females may grow larger and heavier than males (max ash-free dry mass- male: 0.10 g, female: 0.19 g). The maximum individual lifespan of H. invalida is roughly 10 months (Norf et al. 2010). H. invalida therefore has an extremely fast reproductive lifespan, which may give it an edge as an invasive species (Krodkiewska et. al, 2023).


Great Lakes Means of Introduction: Hypania invalida has a moderate probability of introduction to the Great Lakes (Confidence level: High).
Potential pathway of introduction: Trans-oceanic shipping (ballast water and biofouling).
This species is present throughout the North Sea basin (lower Rhine) and Baltic Sea basin (Grigorovich et al. 2003), both origins for high volumes of Great Lakes shipping traffic. Ricciardi and Rasmussen (1998) list H. invalida as the only Ponto-Caspian polychaete likely to be transported to the Great Lakes via ballast water. Submerged ship pumps have taken in larval specimens without being harmed; these worms then rapidly colonized every flume and bowl attached to the inward flow (Norf et al. 2010). Current Great Lakes ballast water regulations (30 ppt flushing) are likely to be effective in reducing the probability of introduction to the Great Lakes (Grigorovich et al. 2003, Norf et al. 2010, Vuckovic et al. 2021).   In Europe, recreational fishermen can have these organisms get stuck in their nets and if not properly disinfected, they will spread to other areas where the nets are used again (Krodkiewska et. al 2023).


Great Lakes Status: Not established in North America, including the Great Lakes

Hypania invalida has a moderate probability of establishment if introduced to the Great Lakes (Confidence level:High).
Hypania invalida has an extensive invasion history throughout Europe (Gherardi et al. 2009), with a spreading pattern that seems to suggest dispersal through a corridor connecting the Danube and Rhine rivers. This species originates in the Ponto-Caspian, a region where climatic conditions are similar to those of the Great Lakes; many other Ponto-Caspian species have successfully invaded the Great Lakes. Other environmental parameters and preferences make most of the Great Lakes basin suitable potential habitat. Sandy bottoms covered with zebra mussel beds also serve as potential habitat  (Norf et al. 2010; Yakovleva and Yakovleva 2010). Food resources, including both diatoms and dreissenind waste products, are widely available in the Great Lakes (Manoleli et al. 1974; Manoleli 1975, Šporka and Nagy 1998; Kurina and Seleznev 2019, Kurina 2023). Reproductive characteristics (high fecundity, short generation time, maternal care, dispersive larvae) greatly increase the odds of establishment and rapid spread (Schroeder and Hermans 1975, Ricciardi and Rasmussen 1998; Bossche et al. 2001;  Bij de Vaate et al. 2002; Devin and Beisel 2007; Norf et al. 2010).


Great Lakes Impacts:
Summary of species impacts derived from literature review. Click on an icon to find out more...

Environmental

There is little or no evidence to support that Hypania invalida has the potential for significant environmental impacts if introduced to the Great Lakes.

Panov et al. (2009) list H. invalida as a white-list species, meaning there is a low risk of it causing significant ecological impacts to introduced areas. There are currently no reports of significant environmental impacts attributed to the presence of this species. Zoric et al. (2010) conclude that this species has limited influence on the overall benthic community. Although in some instances very dense populations have been recorded (46,875 ind/m2), these are without mention of impact on other species (Popescu-Marinescu 1992; Norf et al. 2010; Pavel et al. 2021.

There is little or no evidence to support that Hypania invalida has the potential for significant socio-economic impacts if introduced to the Great Lakes.

Hypania invalida has moderate potential for benefit to the Great Lakes.
Hypania invalida was intentionally introduced to areas of the Volga River in the 1950s-1960s to enhance the nutrition base for tank-raised fish (Dzuban and Slobodchikov 1980). However, this practice has not been repeated and there were no reports of significant benefits from the introductions. H. invalida has the potential to improve water quality by decreasing the amount of organic matter in sediment and water, and can promote the activity of aerobic bacteria by incorporating pockets of air in the sediment (Krodkiewska et al., 2023).


Management: Regulations
This species is not on the Illinois Aquatic Life Approved Species List and if it is not otherwise native to Illinois it is illegal to be imported or possessed alive without a permit (515 ILCS 5/20-90).
Ballast water regulations applicable to this species are currently in place to prevent the introduction of nonindigenous species to the Great Lakes via shipping. See Title 33: Code of Federal Regulations, Part 151, Subparts C and D (33 CFR 151 C) for the most recent federal ballast water regulations applying to the Great Lakes and Hudson River.
Note: Check federal, state/provincial, and local regulations for the most up-to-date information.

Control
There are no known control methods for this species.
Note: Check state/provincial and local regulations for the most up-to-date information regarding permits for control methods. Follow all label instructions.


References (click for full reference list)


Author: Baker, E., K. Dettloff, A. Bartos and R. Sturtevant


Contributing Agencies:
NOAA GLRI Logo


Revision Date: 2/3/2026


Citation for this information:
Baker, E., K. Dettloff, A. Bartos and R. Sturtevant, 2026, Hypania invalida (Grube, 1860): U.S. Geological Survey, Nonindigenous Aquatic Species Database, Gainesville, FL, and NOAA Great Lakes Aquatic Nonindigenous Species Information System, Ann Arbor, MI, https://nas.er.usgs.gov/queries/greatlakes/FactSheet.aspx?Species_ID=3610&Potential=Y&Type=2, Revision Date: 2/3/2026, Access Date: 3/8/2026

This information is preliminary or provisional and is subject to revision. It is being provided to meet the need for timely best science. The information has not received final approval by the U.S. Geological Survey (USGS) and is provided on the condition that neither the USGS nor the U.S. Government shall be held liable for any damages resulting from the authorized or unauthorized use of the information.