|A live individual of Anodonta anatina, the duck mussel|
Unionoida is a monophyletic order of freshwater mussels, aquatic bivalve molluscs. The order includes most of the larger freshwater mussels, including the freshwater pearl mussels. The most common families are the Unionidae and the Margaritiferidae. All have in common a larval stage that is temporarily parasitic on fish, nacreous shells, high in organic matter, that may crack upon drying out, and siphons too short to permit the animal to live deeply buried in sediment.
Families, genera, and species in the order Unionoida are found on six continents, where they are restricted exclusively to freshwater rivers, streams, creeks and some lakes. There are approximately 900 species worldwide. Around 300 species of these freshwater mussels are endemic to North America. Unlike other bivalve orders, Unionoida has no marine species, although one species (Glebula rotundata) tolerates brackish water. This widespread trait and its global distribution suggests the group has inhabited freshwater throughout its geologic history.
Unionoida burrow into the substrate in clean, fast flowing freshwater water rivers, streams and creeks, with their posterior margins exposed. They pump water through the incurrent aperture, obtaining oxygen and filtering food from the water column. Freshwater mussels are some of the longest-living invertebrates in existence. These clams have, like all bivalve mollusks, a shell consisting of two parts that are hinged together, which can be closed to protect the animal's soft body within. Like all mollusks, the freshwater mussels have a muscular "foot", which enables the mussel to move slowly and bury itself within the bottom substrate of its freshwater habitat.
Unionoida have a unique and complex life cycle involving parasitic larvae. This larval form used to be described as "parasitic worms" on the fish host, however, the larvae are not "worms" and do not harm fish under normal circumstances. Most of these freshwater mussel species have separate sexes (although some species, such as Elliptio complanata, are known to be hermaphroditic). The sperm is ejected from the mantle cavity through the male's excurrent aperture and taken into the female's mantle cavity through the incurrent aperture. Fertilised eggs move from the gonads to the gills (marsupia) where they further ripen and metamorph into glochidia, the first larval stage. Mature glochidia are released by the female and then attach to the gills, fins or skin of a host fish. Typically, the freshwater mussel larvae (glochidia) have hooks, which enable the individual to attach itself to fish. Some freshwater mussels release their glochidia in mucilaginous packets called conglutinates. The conglutinate has a sticky filament that allows it to adhere to the substrate so it is not washed away. There is also an even more specialized way of dispersal known as a super-conglutinate. The super-conglutinate resembles an aquatic fly larva or a fish egg, complete with a dark area that looks like an eyespot, and it is appetizing to fish. When a fish consumes it, it breaks up, releasing the glochidia. Mussels that produce conglutinates and super-conglutinates are often gill parasites, the glochidia attaching to the fish gills to continue their development into juveniles. A cyst is quickly formed around the glochidia, and they stay on the fish for several weeks or months before they fall off as juvenile freshwater mussels which then bury themselves in the sediment. This unique life cycle allows Unionoida freshwater mussels to move upstream with the fish host species.
Conservation issues and endangered species status
Many of these freshwater mussel species face conservation issues due to habitat degradation and in some cases due to over-exploitation for the freshwater pearl industry, and for the nacre of their shells, which was used in button manufacturing. Of the North American Unionoida about 70% are either extinct (21 species), endangered (77 species), threatened (43 species) or are listed as species of special concern (72 species).
These bivalve mollusks were heavily exploited for freshwater pearls, and for their nacre which was used in the button manufacturing industry in the late 19th and early 20th centuries. The effects of heavy fishing for freshwater mussels in North America in for use in manufacturing buttons put many of these species close to extinction.
Freshwater pearl industry
The "pearl rush" in North America occurred in the mid to late 1800s as people could easily find freshwater mussels in rivers and streams by "pollywogging" for mussels, some of which had freshwater pearls which they could sell for a significant price. The art of "pollywogging" involves shuffling one's feet in the mud feeling around for freshwater mussels. Because this was relatively easy to do, and an easy way to make money from freshwater selling pearls, this period has been euphemistically called the "pearl rush", and some historians have compared it to the gold rush in California. A formal freshwater mussel fishing industry was established in the mid-1850s to take advantage of this natural resource. The "pearl rush" to find freshwater pearls became so intense in some rivers that literally millions of freshwater mussels were killed in a few years. In some rivers and streams entire freshwater mussel beds were completely eliminated. Although the negative impact of the "pearl rush" on freshwater mussel populations was significant, in the cold light of history it was relatively minor compared to the over fishing that took place just a few years later with the "pearl" button industry.
Freshwater pearls from North America come from freshwater mussels primarily in the family Unionidae. About 20 different species of Unionidae are commercially harvested for pearls. The common names of the most prolific pearl-bearing species include: the butterfly, ebony, elephant ear, heelsplitter, mapleleaf, three-ridge pigtoe, pimple back, pistol grip, and washboard. While white is the most common color, freshwater pearls are valued in part for their wide range of lustrous colors, including: blue, bronze, brown, copper, cream, green, lavender, pink, purple, red, salmon, silvery white, white, and yellow. The different colors of freshwater pearls are primarily a function of which species of freshwater mussel they were formed in, although various factors including position of the pearl nucleus in the shell, water quality, and species type all affect the color of the freshwater pearl.
With the decline in the numbers of native freshwater mussels in North America people began to culture freshwater pearls; this became a big industry in Japan. Natural freshwater pearls are rarely perfectly round, more often than not freshwater pearls are naturally shaped as baroque, slug, or wing shaped. Round pearls are sought after as more desirable for use in jewelry. The shape of the "seed" or nucleus of the freshwater pearl, and the position of the "seed" in the mussel determines the ultimate shape the cultured pearl will take, hence with careful advanced planning cultured pearls can be made round. Cultured pearls have a similar color to natural pearls as the nacre is laid down by the mantle of the freshwater mussel, and thus the color of the pearl may be species specific. Exportation of freshwater mussels for the use in the Japanese cultured pearl industry has supported the North American freshwater mussel fisheries since the late 1950s. The mother of pearl (or nacre) from exported freshwater mussels are used to make a bead nucleus which is placed in a living animal to form a pearl. In the 1990s, the United States exported $50 million worth of freshwater mussel shells to Japan. Exports of freshwater mussel shells declined so that by 2002 the annual revenue of freshwater mussel exportation to Japan had dropped to $35 million. By 1993 in the United States 31 different states were still reporting production of freshwater pearls and export of freshwater mussel shells, including: Alabama, Arkansas, Georgia, Illinois, Indiana, Iowa, Kentucky, Louisiana, Minnesota, Missouri, Nebraska, North Dakota, Oklahoma, South Carolina, South Dakota, Tennessee, Texas, and Wisconsin. To this date the bulk of the freshwater mussel shell and freshwater pearl production comes from Alabama, Arkansas, Louisiana, and Tennessee.
In 1963 the first experimental United States freshwater mussel cultured pearl farm was established in Tennessee by John Latendresse, who is widely proclaimed as "the father of the U.S. cultured freshwater pearl industry." Over the course of nearly 30 years, John Latendresse devoted his money, time and effort to research and develop the cultured freshwater pearl industry in the United States. There are currently six freshwater cultured pearl farms in Tennessee and one in California to support the increasing popularity and demand of freshwater pearl jewelry with consumers in the United States.
Button manufacturing industry
The North American button industry began with a German craftsman named John Boepple, who had made buttons from seashells, horns and antlers in his native country. John Boepple immigrated to the United States in 1887 and found that there were vast beds of thick freshwater mussel shells in Muscatine, Iowa, which he determined were perfect for making "pearl buttons". By 1891, Boepple had set up a shop and was in business as a craftsman making buttons. John Boepple's buttons became popular locally and to ward off competition he was very protective of the secrets of his trade. Since freshwater mussels were so common and the profit potential in making "pearl" buttons was so high, some of Boepple's staff who knew his techniques were "recruited" by other businessmen to start competing businesses. Within a few years there were button factories along the length of the Mississippi River.
The need to "catch" freshwater mussels for the "pearl" button industry spurred the invention of tools to make the job easier than "pollywogging" with bare feet. In 1897 inventive mussel fishermen bent steel bars into wide open hooks which they called "brail hooks" or "crow foots" and used them to try to catch or trap the freshwater mussels. The process was simple: several of these "brail hooks" were attached to a long wooden bar with lengths of rope and the entire assembly was lowered into the river and dragged behind a boat along the river bottom. When the tips of these hooks came in contact with an "open" freshwater mussel, the mussel clamped its valves shut around the hooks and could be lifted from the bottom. Within a short period of time millions of freshwater mussels were collected in this manner.
By 1899, there were sixty button factories in the river states of Illinois, Iowa, Missouri, and Wisconsin, employing 1,917 people. Millions of "pearl" buttons were made annually. This new button industry quickly placed a huge ecological demand on the freshwater mussels of the Midwestern United States. In 1899, clammers harvested over sixteen million pounds of freshwater mussel shells in Wisconsin alone, and the harvest of freshwater mussels in the late 1890s numbered in the tens of millions of pounds per year. Freshwater mussel beds which had previously been so dense as to virtually "carpet" miles of river bottom were almost completely harvested, leaving just a few living freshwater mussels per mile. In 1908, in what was deemed a drastic response to the rapidly declining freshwater mussel population, the U.S. Bureau of Fisheries established a mussel propagation program at the Fairport Biological Station. The purpose of this program was to regulate the overharvesting of freshwater mussels. Freshwater mussels are slow growing sessile organisms, and their reproduction is complex. The button industry in North America was in trouble because years of overharvesting the freshwater mussels had caused a shortage of freshwater mussels and pushed many of the species close to extinction. The invention of plastic and its use in manufacturing buttons during World War II replaced shell "pearl" buttons as the most popular product, and foreshadowed the end of the pearl button manufacturing business.
The superfamilies and families in the order Unionoida, as listed by Bieler et al (2010). The use of † indicate families and superfamilies that are extinct.
- Superfamily †Archanodontoidea Modell, 1957 (placement in Unionoida uncertain)
- Family †Archanodontidae Modell, 1957
- Superfamily Etherioidea Deshayes, 1832
- Superfamily Hyrioidea Swainson, 1840
- Superfamily †Trigonioidoidea Cox, 1952
- Superfamily Unionoidea Rafinesque, 1820
- Family Unionidae Rafinesque, 1820 (Less than 700 species)
- Family Liaoningiidae Yu & Dong, 1993 (placement uncertain)
- Family Margaritiferidae Henderson, 1929 (Presumably less than 10 species) (syn:Margaritaninae, Cumberlandiinae, Promargaritiferidae)
- Family †Sancticarolitidae Simone & Mezzalira, 1997
- Unionoida. Retrieved through: World Register of Marine Species on 3 February 2009.
- Bieler R., Carter J.G. & Coan E.V. (2010). Classification of Bivalve families. Pp. 113–133, in: Bouchet P. & Rocroi J.-P. (2010), Nomenclator of Bivalve Families. Malacologia 52(2): 1–184.
- Huber, Markus (2010). Compendium of Bivalves. A Full-color Guide to 3,300 of the World's Marine Bivalves. A Status on Bivalvia after 250 Years of Research. Hackenheim: ConchBooks. pp. 901 pp. + CD. ISBN 978-3-939767-28-2.
- Haag, Wendell R. (2012). North American Freshwater Mussels: Natural History, Ecology, and Conservation. Cambridge University Press. ISBN 978-0521199384.
- Skinner, A., Young, M. and Hastie, L. (2003) Ecology of the Freshwater Pearl Mussel. Conserving Natura 2000 Rivers. Ecology Series No. 2. English Nature, Peterborough.
- Burnie, D. (2001) Animal. Dorling Kindersley, London.
- Watters, G. T. (1999). Morphology of the conglutinate of the Kidneyshell Freshwater Mussel, Ptychobranchus fasciolaris. Invertebrate Biology 118(3) 289-95.
- Hartfield, P. and E. Hartfield. (1996). Observations on the conglutinates of Ptychobranchus greeni (Conrad, 1834) (Mollusca: Bivalvia: Unionoidea). American Midland Naturalist 135(2) 370-75.
- Piper, Ross (2007), Extraordinary Animals: An Encyclopedia of Curious and Unusual Animals, Greenwood Press.
- See Fish & Wildlife Service, Threatened and Endangered Species Listing, at: 
- Williams, J.D., M.L. Warren, Jr., K.S. Cummings, J.L. Harris, and R.J. Neves (1993). Conservation status of freshwater mussels of the United States and Canada. Fisheries 18(9): 6–22. doi:10.1577/1548-8446(1993)018<0006:CSOFMO>2.0.CO;2.
- Coker, R.E. 1919. Fresh-water mussels and mussel industries of the U.S. Bulletin of the Bureau of Fisheries [Issued separately as U.S. Bureau of Fisheries Document 865]. 36(1917–18): 13–89 + 46 plates.
- Cochran, T. G. II, and J. B. Layzer. 1993. Effects of commercial harvest on unionid habitat use in the Green and Barren rivers, Kentucky. In Conservation and Management of Freshwater Mussels. K. S. Cummings, A. C. Buchanan, and L. M. Koch (eds.). Proceedings of a UMRCC symposium, 12–14 October 1992, St. Louis , MO, Upper Mississippi River Conservation Committee, Rock Island, IL, p. 61-65.
- See: MUSSELS: Washboards, Buttons and Pearls, at Archived 8 June 2010 at the Wayback Machine.
- Olson, Donald (17 July 2002). "Pearls". United States Geological Survey. Retrieved 21 April 2009.