American gizzard shad explained

The American gizzard shad (Dorosoma cepedianum), also known as the mud shad, is a member of the herring family of fish and is native to large swaths of fresh and brackish waters in the United States of America,[1] as well as portions of Quebec, Canada, and Mexico.[2] The adult has a deep body, with a silvery-green coloration above fading to plain silver below.[3] The gizzard shad commonly resides in freshwater lakes, reservoirs, rivers, and streams but can also reside in brackish waters, as it does on the Atlantic coast of the United States. Their range is across most of the continental United States, although they typically go no further north than New York and no further west than New Mexico.[1] They are a large part of many of the ecosystems they inhabit and can drive changes in phyto- and zooplankton, thereby indirectly affecting other planktivorous fishes.[4] The gizzard shad has been widely used as a food source for game fish, with varied success in management and effectiveness.

Physical description

thumbThe gizzard shad's dorsal fin starts behind the insertion of the pelvic fins, and the last ray is greatly lengthened. They have a long anal fin, with 25 to 36 long, soft rays on the fin.[5] The mouth of the gizzard shad has a short, wide, upper jaw with a deep notch along the ventral margin, and a weak, relatively smaller, lower jaw. The mouth itself is subterminal to inferior (on the lower portion of the head), and the adults possess no teeth.[6] The gizzard shad also has 90 to 275 gill rakers along the lower limbs. Their ventral (pelvic) fins are in the thoracic position, or in the chest region of the fish. The gizzard shad can range from very small size when fry to a maximum recorded length of 477mm and maximum weight of 1.56kg (03.44lb).[7] The average length is typically larger in northern waters, and ranges from 284mm at age three years to 399mm at age 10. They have a branched lateral line system that is confined to the head and anterior body, similar to the lateral line systems of other clupeids.[8]

The gizzard shad is brown or gray dorsally, becoming whitish ventrally.[5] A humeral spot, sometimes with purple iridescence,[9] may be faintly visible posterior to the upper operculum.[5] [9] The fish is often slimy.[5]

Range and habitat

Gizzard shad have historically ranged from North Dakota in the northwest of the United States south to New Mexico in the southwest, east to Florida in the southeast, and north to 40°N latitude (they have historically been seen no farther north than the lower New York Harbor). They were not seen in many of the Great Lakes until the late 1800s and early 1900s, although they are suspected to be native to Lake Erie, reaching it after the last ice age. Gizzard shad typically live in lakes and reservoirs, although they can live in rivers and streams, and brackish waters. They reside in the limnetic zone, and can comprise up to 80% of fish biomass in certain lake systems. They prefer shallow lakes with muddy bottoms and relatively high turbidity. This may be due in part to their breeding preferences, but it probably arises from the fact that they have lower survival rates in clear waters and waters with high vegetative cover.[10]

Diet and feeding habits

Gizzard shad are planktivorous in early life, feeding mainly on phytoplankton and zooplankton, such as periphyton, chrysophyta and rotifera, as larvae.[11] Consumptive demand of young of year fish (including larvae) can be intense enough to cause collapses in the zooplankton community, which has far-reaching effects through the ecosystem of which they are a part. In midwestern USA reservoirs, where gizzard shad are often the most abundant fish (by biomass), they usually switch to diets dominated by sediment detritus during the first year of life,[12] whereas in some natural lakes they may rely heavily on zooplankton throughout their lives.[13] As zooplankton are a nutritionally superior food than detritus, if large zooplankton (e.g., Daphnia) are available, gizzard shad probably prefer to feed on this resource. However, in many reservoirs, large zooplankton are scarce so gizzard shad rely on detritus. Gizzard shad growth rates may be lower when they feed only on detritus (compared to zooplankton), and in reservoirs they may consume more zooplankton (and less detritus) when density of conspecifics is low and the abundance of large-bodied zooplankton is high.[14] In such cases, Daphnia and other crustaceans make up a large portion of some gizzard shad diets. Sediment and sand are also ingested by the gizzard shad, which helps it digest food in its muscular gizzard.

Gizzard shad feed mainly during the day, with minimal activity at night. They have been observed at night in Lake Mead, Arizona congregating in schools in very shallow water two to three feet deep during the fall.

Reproduction

The start of the spawning period is typically between mid-May and early June, and is triggered by rising water temperatures. The number of eggs per individual varies between populations, but typically it is 12,500 eggs for a two-year-old and peaks at 380,000 eggs for a four-year-old. The eggs are laid in shallow water in clumps, with seemingly no pairing off occurring between individuals. They spawn during the evening and the early hours of the night, and the eggs adhere to underwater vegetation and do not receive any parental attention. Feeding begins three to four days after hatching, and most individuals are 3.3 mm long upon hatching. Gizzard shad have very high fecundity and a rapid growth rate, meaning they can become a large part of an ecosystem, in terms of abundance and biomass, very quickly.[15] They are capable of hybridizing with the closely related threadfin shad (Dorosoma petenense).

Fisheries management

Gizzard shad were introduced into many lake and river systems as a source of food for game fish, such as walleye, bass, and trout, because of their small size and relatively high abundance. They were thought to be easy food for game fish and could help increase the numbers of fish available, as well as decrease the pressures on prey species (such as the bluegill).[16] However, due to their rapid growth, they can quickly grow beyond the size available to many fish. They remain vulnerable to predation by piscivorous birds, such as great blue herons, as well as raccoons and other wetland predators.[17]

In addition, gizzard shad spawn in large numbers and can reach densities high enough to ensure that many of them survive past the first year, making them essentially invulnerable to fish predation. They can also be harmful exploitative competitors to other species, leading to declines in other fish species' populations.[18] Partly as a result of this, large gizzard shad are sometimes labeled as "nuisances" and "unwanted".[19] However, gizzard shad can help to control populations of zooplankton and insect larvae in productive ecosystems through their unique capabilities as predators of small organisms.

Lake management

Gizzard shad can increase productivity in an ecosystem through redistribution of nutrients, particularly in their adult stages when they consume detritus in lower depths of the lake and both make them available to other predator species as well as excreting them in more bioavailable forms.[20] Because of this, gizzard shad can have a strong effect on algal production even when phosphorus loading from watersheds is high, and can counteract management efforts to combat cultural eutrophication.

Aquatic toxicology

Gizzard shad are important to toxicology testing for chemical products. Due to the food web dependencies and fecundity gizzard shad are somewhat the water bound version of "canary in the coal mine."[21]

Etymology

The gizzard shad is so named because it possesses a gizzard, a sack filled with rocks or sand, that aids the animal in the breakdown of consumed food. Its generic name, Dorosoma, is a reflection of the fact that, when young, the fish has a lancelet-shaped body (doro meaning lanceolate and soma meaning body). The specific name, cepedianum, is a reference to amateur French ichthyologist La Cépède.

Notes and References

  1. Wuellner . Melissa R. . Graeb . Brian D.S. . Ward . Matthew J. . Willis . David W. . 2008 . Review of Gizzard Shad Population Dynamics at the Northwestern Edge of Its Range . American Fisheries Society Symposium . 62 . 637–653 . 26 July 2022.
  2. Web site: Dorosoma cepedianum (Lesueur, 1818). P. Fuller. M.E. Neilson. K. Hopper. U.S. Geological Survey. Nonindigenous Aquatic Species Database. Gainesville, Florida. 30 August 2023. Peer reviewed on 12 April 2013. 15 October 2023.
  3. Miller . Robert Rush . 1957 . Origin and Dispersal of the Alewife, Alosa Pseudoharengus, and the Gizzard Shad, Dorosoma Cepedianum, in the Great Lakes . Transactions of the American Fisheries Society . 86 . 1 . 97–111 . 10.1577/1548-8659(1956)86[97:OADOTA]2.0.CO;2 . 2027.42/141231 . 26 July 2022.
  4. Shepherd . William C. . Mills . Edward L. . 1996 . Diel Feeding, Daily Food Intake, and Daphnia Consumption by Age-0 Gizzard Shad in Oneida Lake, New York . Transactions of the American Fisheries Society . 125 . 3 . 411–421 . 10.1577/1548-8659(1996)125<0411:DFDFIA>2.3.CO;2.
  5. Book: Gizzard Shad (Dorosoma cepedianum) - Native, adapted from A Pictorial Guide to Freshwater Fishes of Connecticut (2009). 20 November 2022. Robert P. Jacobs. Eileen B. O'Donnell. Connecticut DEEP. 2009 . Connecticut Department of Environmental Protection . 978-0942085150. Connecticut Department of Energy & Envionrmental Protection.
  6. Web site: Hansen . Paul . Kitchell . James . Lyons . John . White . Elizabeth . Moy . Phil . Gen . Yael . Dellinger . Rich . Fish ID: Shad, Gizzard . 2022-07-25 . University of Wisconsin Sea Grant Institute.
  7. Williamson . Kathryn L. . Nelson . Patrick C. . 1985 . Habitat suitability index models and instream flow suitability curves: Gizzard Shad . U.S Fish and Wildlife Services Biological Reports . 82 . 10.112 . 1–33 . 25 July 2022.
  8. Stephens . Robert R. . The Lateral Line System of the Gizzard Shad, Dorosoma cepedianum Lesueur (Pisces: Clupeidae) . Copeia . 1985 . 3 . 540–556 . 1985 . 10.2307/1444742. 1444742 .
  9. Web site: South Carolina Department of Natural Resources. Gizzard shad (Dorosoma cepedianum) - Native. South Carolina DNR. Duane Raver. 2015. 20 November 2022.
  10. Michaletz . Paul H. . Bonneau . Joseph L. . 2005 . Age-0 Gizzard Shad Abundance is Reduced in the Presence of Macrophytes: Implications for Interactions with Bluegills . Transactions of the American Fisheries Society . 134 . 1 . 149–159 . 10.1577/FT04-011.1.
  11. Web site: Morris . Christina . Dorosoma cepedianum - Eastern gizzard shad . .
  12. Higgins. Karen A.. Vanni. Michael J.. González. Maria J.. 2006. Detritivory and the stoichiometry of nutrient cycling by a dominant fish species in lakes of varying productivity. Oikos. en. 114. 3. 419–430. 10.1111/j.2006.0030-1299.14745.x. 1600-0706.
  13. Gu. B.. Schelske. C. L.. Hoyer. M. V.. 1996. Stable isotopes of carbon and nitrogen as indicators of diet and trophic structure of the fish community in a shallow hypereutrophic lake. Journal of Fish Biology. en. 49. 6. 1233–1243. 10.1111/j.1095-8649.1996.tb01792.x. 1095-8649.
  14. Schaus . Maynard H. . Vanni . Michael J. . Wissing . Thomas E. . 2002 . Biomass-Dependent Diet Shifts in Omnivorous Gizzard Shad: Implications for Growth, Food Web, and Ecosystem Effects . Transactions of the American Fisheries Society . 131 . 1 . 40–54 . 10.1577/1548-8659(2002)131<0040:BDDSIO>2.0.CO;2 . 10.1.1.487.3857 .
  15. Irwin . Brian J. . DeVries . Dennis R. . Kim . Gene W. . 2003 . Responses to Gizzard Shad Recovery following Selective Treatment in Walker County Lake, Alabama, 1996-1999 . North American Journal of Fisheries Management . 23 . 4 . 1225–1237 . 10.1577/M02-068.
  16. Zweifel . Richard D. . Hale . R. Scott . Bunnell . David B. . Bremigan . Mary T. . 2009 . Hatch Timing Variations among Reservoir Gizzard Shad Populations: Implications for Stocked Sander spp. Fingerlings . North American Journal of Fisheries Management . 29 . 2 . 488–494 . 10.1577/M08-141.1.
  17. Web site: Field Guide: Gizzard Shad . Missouri Department of Conservation . 25 July 2022.
  18. Garvey . James E. . Stein . Roy A. . 1998 . Linking Bluegill and Gizzard Shad Prey Assemblages to Growth of Age-0 Largemouth Bass in Reservoirs . Transactions of the American Fisheries Society . 127 . 1 . 70–83 . 10.1577/1548-8659(1998)127<0070:LBAGSP>2.0.CO;2 . 26 July 2022. 1811/45408 . free .
  19. Web site: Fish Surveys. 2022. 26 July 2022. EnviroScience. en-US.
  20. Williamson. Tanner J.. Vanni. Michael J.. González. María J.. Renwick. William H.. Bremigan. Mary T.. Conroy. Joseph D.. 2018-09-01. The importance of nutrient supply by fish excretion and watershed streams to a eutrophic lake varies with temporal scale over 19 years. Biogeochemistry. en. 140. 2. 233–253. 10.1007/s10533-018-0490-6. 104550667 . 1573-515X.
  21. Web site: Akerman. James W.. 10 August 1988. Gizzard Shad Mortalities in Bifenthrin Study Pond. live. https://web.archive.org/web/20170216020931/https://archive.epa.gov/pesticides/chemicalsearch/chemical/foia/web/pdf/128825/128825-053.pdf . 16 February 2017 . 26 July 2022. U.S. Environmental Protection Agency.