Orthione griffenis

Invasion History

First Non-native North American Tidal Record: 1988
First Non-native West Coast Tidal Record: 1988
First Non-native East/Gulf Coast Tidal Record:

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General Invasion History:

Orthione griffenis was first described from specimens collected from Upogebia pugettensis (Blue Mud Shrimp), from Yaquina Bay, Oregon, in 1999–2000 (Markham 2004). Adults of this isopod inhabit the gill chamber of the mud shrimp, while feeding on its blood, thereby reducing the shrimp's reproductive potential (Floyd and Chapman 2005; Dumbauld et al. 2011; Chapman et al. 2012). Based on its recent discovery, especially on an animal which is widely studied and used for bait (U. pugettensis), O. griffenis is suspected to be introduced to Northeast Pacific waters (Floyd and Chapman 2005). Prior to its description, O. griffenis was recognized from waters of the Yellow Sea, China, from specimens of the mud shrimp Austinogebia wushienweni collected from 1951 to 1959, from A. narutensis and U. issaeffi in the Seto Inland Sea in Japan (Williams and An 2009), and from U. major in the Yellow Sea, Korea (Hong et al. 2015). In the Northeast Pacific, it has been found on U. pugettensis from Vancouver, British Columbia to Morro Bay, California (Williams and An 2009; Chapman et al. 2012) and most recently near Ketchikan up to Sitka, Alaska (Chapman and Johnson, personal communication, Chapman et al. 2021; GBIF 2024), and on U. macginitieorum in Carpinteria, California and Todos los Santos Bay, Baja California, Mexico. This parasite has been associated with the decline and extinction of many West Coast populations of U. pugettensis (Chapman et al. 2012).

Hong et al. (2015), compared mitochondrial CIO genes from Korean and Oregon specimens and argues that the Eastern and Western populations are conspecific, but represent disjunct populations of an amphi-Pacific species. This hypothesis seems improbable based on the history given above, but a larger survey would provide greater understanding of biogeographical range and origin of this species.

North American Invasion History:

Invasion History on the West Coast:

The earliest reported specimens of O. griffenis on the West Coast were collected in 1988 in Willapa Bay, Washington (WA) (Dumbauld et al. 2011; Chapman et al. 2012), and subsequently in Morro Bay, California (CA) in 1992. Specimens were photographed in 1995 and 1997 on U. pugettensis from Eld Island, WA and Coos Bay, Oregon (OR) respectively (Chapman et al. 2012), before the collection of the formally described specimens from Yaquina Bay, OR in 1999 (Markham 2004). Between 2000 and 2008, it was collected on U. pugettensis from Vancouver Harbor and Vancouver Island, British Columbia (Lamb and Hanby 2005, cited by Williams and An 2009; Chapman et al. 2012); Grays Harbor, WA; Willapa Bay, WA; Tillamook Bay, OR; Netarts Bay, OR; Alsea Bay, OR; Yaquina Bay, OR; Coos Bay, OR; Humboldt Bay, CA; and Bodega Harbor, CA (Chapman et al. 2012). Further south, O. griffenis was found on U. macginitieorum in Carpinteria, CA in 2003, and Todos los Santos Bay, Baja California, Mexico in 2008. In Alaska, O. griffenis was found near Ketchikan in 2017, and has subsequently been found farther north near Sitka in 2021 (Chapman and Johnson, personal communication; GBIF 2024). Recent research has been able to age Orthione and suggests that the 2017 Alaskan specimen was probably 3 years old (Chapman, manuscript in prep). In the bays where this parasite was found, populations of U. pugettensis have declined sharply or disappeared (Chapman et al. 2012). Effects on populations of U. macginitieorum are less clear. The parasite has not been reported from two other Southern California-Mexico species, U. lepta and U. onchyon (Chapman et al. 2012). The likely initial vector for the introduction was ballast water containing the planktonic epicaridium, microniscus or cryptoniscus larvae of the isopods. Upogebia pugettensis is widely harvested and sold as bait, which is a likely means of transport between estuaries.

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Description

Orthione griffenis is a bopyrid isopod. Members of the family Bopyridae are highly modified isopods, whose adults are sessile parasites on decapod crustaceans. Males and females are dramatically different, but both are segmented, and have recognizable pereiopods. Females are large and asymmetrical, while males are small and symmetrical. In both sexes, the cephalon (head), peraeon (thorax), and pleon (abodomen) are distinct (Schultz 1969; Markham 1985). Eyes are absent in adult females, and are small in juvenile females and males (Markham 2004; Williams and An 2009).

Female O. griffensis are 6–24 mm long and lack pigment. Females have a broadly oval body, with moderate asymmetry. In dorsal view, the body is somewhat pulled out in the right-posterior direction. The head is squarish-ovate, and continuous with the peraeon. Frontal laminae extend across the anterior of the head. The first antenna consists of five segments extended beyond the margin of the head. The 2nd antenna is greatly reduced, and comprised of three segments. The barbula (in Bopyridae, the posterio-ventral border of the head, often with one or more beardlike projections (Markham 1988)) has a single claw-shaped process on each side of the head. The maxilliped is roughly triangular and lacks a palp, and its plectron (anteromedial spur) is blunt.

The peraeon is widest across peraeonites 4–5. Peraeonite 1 is shortest and strongly curved around the head, peraeonite 2 is strongly concave anteriorly, while peraeonites 5–7 are strongly concave posteriorly. Pereonites 1–6 are bordered by coxal plates. Peraeonites 2–5 have a central, dorsal depression. On the ventral side of the body, 5 pairs of oostegites cover the brood pouch, the first pair being nearly circular and the subsequent pairs long and slender. The pereiopods are relatively short and blunt, but have all their joints distinct, and are double in size posteriorly. The bases of the pereiopods are developed into carinae (keels) and the dactyls (segment 7) are short comma-shaped claws, fitting into receptacles on the propodi (segment 6). The pleon (abdomen) consists of 6 pleonites, all concave posteriorly. On the ventral side, the borders of the pleonites are covered by slender uniramous lateral plates and biramous pleopods, all of similar size.

Male O. griffenis are smaller than females, around 4.5–11 mm long.  They have a symmetrical body, with a semicircular head, a pleon of 7 segments, straight parallel sides, and a rounded pleon of 6 segments. Males from North America lacked eyes (Markham 2004), but males from China had small, dark eyes (Williams and An 2009). There is a short pair of antennae 1, and a longer pair of antennae 2, extending beyond the margins of the head. The pereiopods are short, clustered medially, with their dactyls are folded against the propodi. The pleonites become progressively narrower, with pleonites 1-5 becoming more convex on the posterior side, and pleonite 6, being small and rounded, and set into the concave space, with a pair of projecting uropods. The above description is based on: Markham 2004 and Williams and An 2009.

Williams and An (2009) illustrate an epicaridium larva of O. griffenis, the stage which hatches from the eggs in the brood pouch. This larva attaches to a copepod, and metamorphoses into a microniscus larva, which molts several times and transforms into a cryptonicus larva, that infects an upogebiid mud shrimp (Schultz 1969; Williiams and An 2009). The cryptoniscus and microniscus stages of O. griffenis have not been described.

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Taxonomy

Ecology

General:

Orthione griffenis, like other bopyrid isopods, is an ectoparasite on decapod crustaceans as an adult, but uses copepods as a host in the larval stages of its life cycle (Markham 2004; Williams and An 2009). The parasitic female releases a planktonic epicaridium larva, which attaches to a copepod and develops into a microniscus larva as it grows through several molts, and then detaches as a cryptonicscus larva and attaches to a thalassiniid mud shrimp (Upogebia, Austinogebia sp.). The larva burrows beneath the carapace of its host, loses its appendages, and becomes a bopyridium. If the shrimp has no previous infestation, the isopod matures as a female; if another O. griffenis is present, the isopod becomes a dwarf male (Repetto and Griffen 2011). In Oregon populations, Repetto and Griffen (2011) found that infected animals had no more than one male-female pair per animal. Females brood and release large numbers of larvae (Williams and An 2009).

The hosts of O. griffenis are mud shrimps of the family Upogebiidae, decapod crustaceans, which reach about 100–150 mm in size and burrow in intertidal mudflats. The adult inhabits the gill chamber of the mud shrimp and feeds on its hemolymph. This parasite does not increase the host's mortality, or feminize males, but the energetic burden greatly reduces reproductive output, effectively castrating the shrimps (Griffen 2009; Smith and Chapman 2009).

Food:

Mud Shrimps (Upogebia spp.)

Consumers:

Competitors:

Trophic Status:

Parasite

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Habitats

General Habitat	Unstructured Bottom	None
General Habitat	Oyster Reef	None
General Habitat	Salt-brackish marsh	None
Salinity Range	Polyhaline	18-30 PSU
Salinity Range	Euhaline	30-40 PSU
Tidal Range	Subtidal	None
Tidal Range	Low Intertidal	None
Tidal Range	Mid Intertidal	None
Vertical Habitat	Endobenthic	None
Vertical Habitat	Planktonic	None

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Life History

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Tolerances and Life History Parameters

Minimum Length (mm)	79	For adult males. The minimum size for adult females is 6 mm (Markham 2004; Williams and An 2009).
Maximum Length (mm)	24	For adult females. The maximum size for males is 11 mm (Markham 2004; Williams and An 2009).
Broad Temperature Range	None	Cold temeprate-Warm temperate
Broad Salinity Range	None	Polyhaline-Euhaline

General Impacts

Adults of Orthione griffenis inhabit the gill chamber of mud shrimps from the family Upogebiidae. It has been found in Austinogebia wushienweni, A. narutensis and Upogebia issaeffi in its native Northwest Pacific range, and in U. pugettensis and U. macginitieorum in the Northeast Pacific (Williams and An 2009; Chapman et al. 2012). Prevalence in one native population, in U. issaeffi, in Vostok Bay, Russia was 4%, but infected females still produced egg clutches (Selin 2014). Impacts on the naive, invaded host, U. pugettensis, appear to be much greater, resulting in the local extinction of mud shrimp populations, and associated ecological and economic impacts, due to the loss of a popular bait animal and an important ecosystem engineer (Dumbauld et al. 2011; Chapman et al. 2012).

Economic Impacts

Fisheries- Upogebia pugettensis is widely used, and commercially harvested, as fish bait in the Northeast Pacific. The total commercial harvest for Oregon coastal bays declined sharply after 1992. In Alsea Bay, in 2009–2011, 120 kg were commercially harvested, compared to 480 kg in 1991–1996 (Chapman and Carter 2014). On the other hand, this mud shrimp is regarded as a pest in oyster beds and is controlled with the pesticide Carbaryl, so that its decline might have benefits for oyster fisheries (Smith et al. 2009). Chapman et al. (2012) have noted that the decline of U. pugettensis has permitted the expansion of oyster areas, such as in Samish Bay, OR, where dense shrimp populations interfered with culture operations.

Ecological Impacts

Parasitism- Juveniles and adults of O. griffenis attach to the interior of the gill chamber of U. pugettensis and sucks the host's blood. Infection results in weight loss, which is positively correlated with weight of the parasite(s) (Smith et al. 2008). Infected ovigerous females are rarely seen, and carry very small broods (e.g., 15 eggs for an infected female vs 1800 for a typical uninfected female; Smith et al. 2008). Impacts of parasitism were greater on female shrimps than on males. Infected females had a reduced Gonado-Hepato Somatic Index (GSHI), consistent with a diversion of metabolic energy from the shrimp's reproduction to the parasite. Male shrimp were infected less frequently than females, had smaller parasites, and their GSHI was not affected by infection. There was no evidence for feminization of males by the parasite (Repetto and Griffen 2011).

Habitat Change- By reducing or eliminating populations of U. pugettensis, Orthione griffenis has had broad impacts on West Coast ecosystems. Upogebia burrows are major habitat structures in mudflats, aerating sediment, suspension-feeding, and providing organic enrichment to sediment (Ferraro and Cole 2007; Smith et al. 2008; Dumbauld et al. 2011).

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Regional Impacts

NEP-IV	Puget Sound to Northern California		Ecological Impact	Parasitism
Orthione griffenis, a bopyrid isopod, inhabits the gill chamber of the mud shrimp Upogebia pugettensis, and sucks its blood, greatly reducing the shrimp's reproductive potential (Floyd and Chapman 2005; Smith et al. 2008; Griffen 2009). In Yaquina Bay, prevalence of these parasites was high 57% for males, 80% for females (Smith et al. 2008). The metabolic costs of parasitism are likely to reduce the abundance of this species in the upper intertidal parts of its range, where feeding time is limited, while animals in the lower intertidal have more food, but also more exposure to the planktonic stages of the parasites (Griffen 2009). A decline in abundance of U. pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009), but the role of the parasite in mortality and reproduction of the shrimp is not clear (Smith et al. 2008; Dumbauld et al. 2011). Griffen (2009) modelled the shrimps' metabolism and reproduction throughout the tidal range, and found evidence that shrimps would be adversely affected both at the upper and lower limits of their tidal range. The decline of Upogebia pugettensis in Willapa Bay showed patterns consistent with a failure of recruitment, due to reproductive castration of adults. Shrimp abundance decreased as the isopod prevalence increased, although isopod parasitism did not affect adult mortality. However, infected shrimp failed to reproduce (Dumbauld et al. 2011). Populations of Upogebia pugettensis in Alsea Bay have been declining, from 1992 to 2011, due to parasitism and castration by Orthione griffenis (Chapman and Carter 2014).
NEP-IV	Puget Sound to Northern California		Ecological Impact	Trophic Cascade
A decline in abundance of Upogebia pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009). The mud shrimp is a major player in the foodweb of northeast Pacific estuaries, as a suspension-feeder and intertidal prey item for birds and fishes, and is also an important ecosystem engineer as a burrower (Smith et al. 2008; Griffen 2009).
P210	Yaquina Bay		Ecological Impact	Parasitism
Orthione griffenis, a bopyrid isopod, inhabits the gill chamber of the mud shrimp Upogebia pugettensis, and sucks its blood, greatly reducing the shrimp's reproductive potential (Floyd and Chapman 2005; Smith et al. 2008; Griffen 2009). In Yaquina Bay, prevalence of these parasites was high 57% for males, 80% for females (Smith et al. 2008). The metabolic costs of parasitism are likely to reduce the abundance of this species in the upper intertidal parts of its range, where feeding time is limited, while animals in the lower intertidal have more food, but also more exposure to the planktonic stages of the parasites (Griffen 2009). A decline in abundance of U. pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009), but the role of the parasite in mortality and reproduction of the shrimp is not clear (Smith et al. 2008).
P210	Yaquina Bay		Ecological Impact	Trophic Cascade
A decline in abundance of Upogebia pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009). The mud shrimp is a major player in the foodweb of northeast Pacific estuaries, as a suspension-feeder and intertidal prey item for birds and fishes, and is also an important ecosystem engineer as a burrower (Smith et al. 2008; Griffen 2009).
NEP-IV	Puget Sound to Northern California		Economic Impact	Fisheries
Upogebia pugettensis is widely used as fishbait in the Pacific Northwest, so that its decline could affect recreational fishing (Floyd and Chapman 2005). Commercial harvests from major Oregon bays declined from 1988 to 2011 (Chapman et al. 2014). On the other hand, this mud shrimp is regarded as a pest in oysterbeds, and is controlled with the pesticide Carbaryll so that its decline might have benefits for oyster fisheries (Smith et al. 2008).
P210	Yaquina Bay		Economic Impact	Fisheries
Upogebia pugettensis is widely used as fishbait in the Pacific Northwest, so that its decline could affect recreational fishing (Floyd and Chapman 2005). On the other hand, this mud shrimp is regarded as a pest in oysterbeds, and is controlled with pesticides, so that its decline might have benefits for oyster fisheries (Smith et al. 2008).
P270	Willapa Bay		Ecological Impact	Parasitism
The decline of Upogebia pugettensis in Willapa Bay showed patterns consistent with a failure of recruitment, due to reproductive castration of adults. Shrimp abundance decreased as the isopod prevalence increased, although isopod parasitism did not affect adult mortality. However, infected shrimp failed to reproduce (Dumbauld et al. 2011).
NEP-III	Alaskan panhandle to N. of Puget Sound		Ecological Impact	Parasitism
Dramatic reductions in populations of Upogebia pugettensis, associated with high prevalence of Orthione griffenis were seen in Barkley and Grappler Sounds, Vancouver Island, in Vancouver Harbor, and in several locations in Puget Sound (Chapman et al. 2012).
P290	Puget Sound		Ecological Impact	Parasitism
Infested U. pugettensis were found as early as 1995, and mud shrimp populations declined in the late 198s and 1990s (Chapman et al. 2012).
P200	Alsea River		Ecological Impact	Parasitism
Populations of Upogebia pugettensis in Alsea Bay have been declining, from 1992 to 2011, due to parasitism and castration by Orthione griffenis (Chapman et al. 2014).
P290	Puget Sound		Economic Impact	Fisheries
The decline of U. pugettensis populations permitted the expansion of oyster culture operations into areas, such as Samish Bay, where oyster culture was not previously possible (Chapman et al. 2012).
P200	Alsea River		Economic Impact	Fisheries
Commerical harvest of Upogebia pugettensis in Alsea Bay has declined from an an annual average of 480 kg in 1991-1996 to 120 kg in 2009-2011 (Chapman et al. 2014).
P270	Willapa Bay		Ecological Impact	Trophic Cascade
A decline in abundance of Upogebia pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009). The mud shrimp is a major player in the foodweb of northeast Pacific estuaries, as a suspension-feeder and intertidal prey item for birds and fishes, and is also an important ecosystem engineer as a burrower (Smith et al. 2008; Griffen 2009).
WA	Washington		Ecological Impact	Parasitism
The decline of Upogebia pugettensis in Willapa Bay showed patterns consistent with a failure of recruitment, due to reproductive castration of adults. Shrimp abundance decreased as the isopod prevalence increased, although isopod parasitism did not affect adult mortality. However, infected shrimp failed to reproduce (Dumbauld et al. 2011)., Infested U. pugettensis were found as early as 1995, and mud shrimp populations declined in the late 198s and 1990s (Chapman et al. 2012).
WA	Washington		Ecological Impact	Trophic Cascade
A decline in abundance of Upogebia pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009). The mud shrimp is a major player in the foodweb of northeast Pacific estuaries, as a suspension-feeder and intertidal prey item for birds and fishes, and is also an important ecosystem engineer as a burrower (Smith et al. 2008; Griffen 2009).
WA	Washington		Economic Impact	Fisheries
The decline of U. pugettensis populations permitted the expansion of oyster culture operations into areas, such as Samish Bay, where oyster culture was not previously possible (Chapman et al. 2012).
OR	Oregon		Ecological Impact	Parasitism
Orthione griffenis, a bopyrid isopod, inhabits the gill chamber of the mud shrimp Upogebia pugettensis, and sucks its blood, greatly reducing the shrimp's reproductive potential (Floyd and Chapman 2005; Smith et al. 2008; Griffen 2009). In Yaquina Bay, prevalence of these parasites was high 57% for males, 80% for females (Smith et al. 2008). The metabolic costs of parasitism are likely to reduce the abundance of this species in the upper intertidal parts of its range, where feeding time is limited, while animals in the lower intertidal have more food, but also more exposure to the planktonic stages of the parasites (Griffen 2009). A decline in abundance of U. pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009), but the role of the parasite in mortality and reproduction of the shrimp is not clear (Smith et al. 2008)., Populations of Upogebia pugettensis in Alsea Bay have been declining, from 1992 to 2011, due to parasitism and castration by Orthione griffenis (Chapman et al. 2014).
OR	Oregon		Ecological Impact	Trophic Cascade
A decline in abundance of Upogebia pugettensis has been observed throughout its range, coinciding with the arrival of the parasite (Griffen 2009). The mud shrimp is a major player in the foodweb of northeast Pacific estuaries, as a suspension-feeder and intertidal prey item for birds and fishes, and is also an important ecosystem engineer as a burrower (Smith et al. 2008; Griffen 2009).
OR	Oregon		Economic Impact	Fisheries
Upogebia pugettensis is widely used as fishbait in the Pacific Northwest, so that its decline could affect recreational fishing (Floyd and Chapman 2005). On the other hand, this mud shrimp is regarded as a pest in oysterbeds, and is controlled with pesticides, so that its decline might have benefits for oyster fisheries (Smith et al. 2008)., Commerical harvest of Upogebia pugettensis in Alsea Bay has declined from an an annual average of 480 kg in 1991-1996 to 120 kg in 2009-2011 (Chapman et al. 2014).
CA	California		Economic Impact	Parasitism
Affecting important bait animal, Upogebia pugetensis
CA	California		Economic Impact	Fisheries
Affecting important bait animal, Upogebia pugettensis (Chapman et al. 2012)

References

Chapman, John W.; Carter, Cameron S. (2014) A rapid intertidal megafauna survey method applied to Upogebia pugettensis, and its introduced parasite, Orthione griffensis, Journal of Crustacean Biology 34(3): 349-356

Chapman, John W.; Dumbauld, Brett R.; Itani, Gyo; Markham, John C. (2012) An introduced Asian parasite threatens northeastern Pacific estuarine ecosystems, Biological Invasions 14: published online

Chapman, John W.; Li, Jingchun; McGowan, Michael F.; Breitenstein, Ralph A.; Appy, Ralph; Hie, Kathryn A.; Piotrowski, Christina N.; Elder, Leanne E. (2021) A doubled down invasion of the northeast Pacific by the Asian mud shrimp,Upogebia major and its coevolved bopyrid isopod parasite, Orthione griffenis, Aquatic Invasions 16(4): 721–749
10.3391/ai.2021.16.4.09

Dumbauld, Brett R.; Chapman, John W.; Torchin, Mark E.; Kuris, Armand M. (2011) Is the collapse of mud shrimp (Upogebia pugettensis) populations along the Pacific coast of North America caused by outbreaks of a previously unknown bopyrid isopod parasite (Orthione griffenis)?, Estuaries and Coasts 34: 336-350

Ferraro, Steven P.; Cole, Faith A. (2007) Benthic macrofauna-habitat associations in Willapa Bay, Washington, USA, Estuarine, Coastal and Shelf Science 71: 491-507

Floyd, Mark; Chapman, John 2005 New invasive parasite raises concern for West Coast estuaries.. <missing URL>



Global Biodiversity Information Facility 2024 GBIF Occurrence Download: Orthione griffenis. https://doi.org/10.15468/dl.9tjyuh



Griffen, Blaine D. (2009) Effects of a newly invasive parasite on the burrowing mud shrimp, a widespread ecosystem engineer, Marine Ecology Progress Series 391: 73-83

Hong, Jae-San; Lee, Chae-Lin; Min, Chi-Sik (2015) Occurrence of Orthione griffenis Markham 2004 (Isopoda: Bopyridae), parasite of the mud shrimp de Haan 1841 in South Korean waters, and its implications with regard to marine bioinvasions, Journal of Crustacean Biology 35(5): 605-615

Markham, John C. (1985) A review of the bopyrid isopods infesting caridiean shrimps in the northwestern Atlantic Ocean, with special reference to those collected in the Hourglass cruises in the Gulf of Mexico, Memoirs of the Hourglass Cruises 7(3): 1-156

Markham, John C. (1988) Descriptions and revisions of some species of Isopoda Bopyridae of the North Western Atlantic Ocean, Zoologische Verhandelingen 246: 1-63

Markham, John C. (2004) New species and records of Bopyridae (Crustacea: Decapoda) infesting species of the genus Upogebia (Crustacea: Decapoda: Upogebiidae): the genera Orthione Markham, 1988, and Gyge Cornalia and Panceri, 1861, Proceedings of the Biological Society of Washington 117(2): 186-198

Repetto, Michele; Griffen, Blaine D. (2011) Physiological consequences of parasite infection in the burrowing mud shrimp, Upogebia pugettensis, a widespread ecosystem engineer, Marine and Freshwater Research 63(1): 60-67

Schultz, G.A. (1969) The Marine Isopod Crustaceans, Wm. C. Brown Company, Dubuque, Iowa. Pp. <missing location>

Selin, N. I. (2014) Some features of the biology of the mud shrimp Upogebia issaeffi (Balls, 1913) (Decapoda: Upogebiidae) from the subtidal zone of Vostok Bay, Sea of Japan, Russian Journal of Marine Biology 40(1): 2-–29

Smith, Andrew E.; Chapman, John W.; Dumbauld, Brett R. (2008) Population structure and energetics of the bopyrid isopod parasite Orthione griffenis in mud shrimp Upogebia pugettensis, Journal of Crustacean Biology 28(2): 228-233

Sol, Sean Y.; Lomax, Daniel P. ; Hanson; Amanda C.; Corbett, Catherine; Johnson, Lyndal L. (2021) Fish communities in the tidal freshwater wetlands of the Lower Columbia River, Northwest Science 94(3-3): Published online

Williams, Jason D.; An, Jianme (2009) The cryptogenic parasitic isopod Orthione griffenis from the eastern and western Pacific, Integrative and Comparative Biology 49(2): 114-126

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