Fundulus grandis ZBK :
- Paul V. Loiselle (2006): A review of the Malagasy Pachypanchax (Teleostei: Cyprinodontiformes, Aplocheilidae), with descriptions of four new species. Zootaxa 1366, 1-44: 42-42, URL:http://www.zoobank.org/urn:lsid:zoobank.org:pub:D12AF7A9-88CB-46F2-9550-2A97D5E91389
occurs (regularly, as a native taxon) in multiple nations
Regularity: Regularly occurring
Type of Residency: Year-round
Global Range: Range includes the North American Atlantic and Gulf coasts from the St. Johns River, Florida, to Laguna de Tamiahua, Veracruz, Mexico, including the northern Gulf of Mexico and Cuba (Lee et al. 1980, Page and Burr 2011).
Length: 14 cm
Catalog Number: USNM 45564
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Fishes
Collector(s): B. Evermann
Year Collected: 1891
Locality: Galveston Bay, Texas., Texas, United States, Galveston Bay, Gulf of Mexico, Atlantic
Habitat Type: Freshwater
Comments: Habitat includes grassy bays, canals, and nearby fresh water; usually these fishes are over mud, near vegetation; they are uncommon in fresh water except far inland in the Brazos River and Rio Grande, Texas (Page and Burr 2011); common along bay shores and tidal marshes in a wide range of salinities, from fresh water (streams) to 76 ppt (Lee et al. 1980); avoids tidal flats (Robins and Ray 1986).
Depth range (m): 1 - 1
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
Non-Migrant: No. All populations of this species make significant seasonal migrations.
Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).
Locally Migrant: No. No populations of this species make annual migrations of over 200 km.
Comments: Eats fishes, aquatic insects, and vegetation. Often in feeding groups of 12-20.
Diseases and Parasites
Number of Occurrences
Note: For many non-migratory species, occurrences are roughly equivalent to populations.
Estimated Number of Occurrences: 81 to >300
Comments: This species is represented by a large number of occurrences (subpopulations).
100,000 to >1,000,000 individuals
Comments: Total adult population size is unknown but very large. This species is common in much of its range.
Life History and Behavior
Spawning season varies geographically; possibly year-round. In Alabama, spawns March-August, mainly during spring tides in March and April, solely during spring tides thereafter (Greeley et al. 1983).
National NatureServe Conservation Status
Rounded National Status Rank: N5 - Secure
NatureServe Conservation Status
Rounded Global Status Rank: G5 - Secure
Global Short Term Trend: Relatively stable (=10% change)
Comments: Trend over the past 10 years or three generations is uncertain but likely relatively stable.
Comments: No major threats are known.
Relevance to Humans and Ecosystems
Comments: Has been used in carcinogenesis testing (Metcalfe 1989).
The Gulf killifish, Fundulus grandis, is one of the largest members of the genus Fundulus; it is capable of growing up to 18 cm in length, whereas the majority of other Fundulus reach a maximum length of 10 cm. Therefore, F. grandis is among the largest minnows preyed upon by many sport fish, such as flounder, speckled trout, and red snapper. Fundulus derives from the Latin meaning "bottom," and grandis means "large". The Gulf killifish is native the Gulf of Mexico from Texas to Florida and the eastern coast of Florida to Cuba in the Atlantic Ocean. Threats to the survival of the Gulf killifish include extreme changes in salinity, changes in temperatures, and toxic events such as the hypoxic dead zone in Louisiana and the Deepwater Horizon oil spill. The Gulf killifish is currently being used to test the effects of oil and oil dispersants on the physiology of marine species affected by these substances. This is significant to conservation biology, because with the continued extraction of oil and other natural resources from North American waters, it has become increasingly important to understand the risks and consequences in worst-case scenarios, such as the Deepwater Horizon oil spill, and the lasting effects on the marine ecosystem.
Fundulus grandis has a unique coloration that separates it from other Fundulus species. First, the base color is a dull greenish above shading to lemon-yellow below. Furthermore, the differences in coloration between males show much more vivid colors with silver flecking and noticeable striping; and females, which can appear olive to dull olive below if they grow big enough. Additionally, stripes, spots, and different colors occur along the body structure. In the predorsal region are predorsal stripes, which may be present, but generally fade as the fish ages  and occasionally predorsal spots. Also, small pearly spots are found along the side of the fish. The anal and lower half of the caudal region may be yellow or the anal, dorsal, and caudal regions may be darker in color with white splotches at the base. Additionally, the coloration of the male fish changes when they are breeding. In all, these males are deep blue dorsally, and have blue median fins with light blue spots and yellow-orange margins. However, in general, the Gulf killifish is characterized by its yellowish or pale belly, and darker back with many pale spots, mottling, and inconspicuous bars.
More than 15 scale rows occur on the killifish’s body between the pelvic fin and the isthmus, as well as 31-39 longitudinal scale rows. Additionally, an average of 17-20 individual scales are seen around the caudal peduncle. Also, 12-19 faint stripes are found along the side of the killifish. The killifish also has five pairs of mandibular pores, which are sensory pores located on the underside of the lower jaw, part of the lateral line sensory system. Around 9-12 gill rakes, 10-12 dorsal rays, 9-11 anal rays, and six pelvic rays are present.
The maximum length of the Gulf killifish is 18.0 cm, but it is usually around 10.4 cm in length. These fish are characterized by a blunt head and short snout. The mouth is positioned nearly terminal and its lower jaw slightly projects outwards. The position of the dorsal fin varies slightly among individuals, yet it generally originates anterior to the anal fin origin. The anal fin of the killifish is rounded, with the base of the fin being more than half the length of its longest rays. The distance from the origin of the dorsal fin to the end of the hypural plate is usually less than the distance from the origin of the dorsal fin to the preopercle; yet occasionally these distances are equal due to the genetic variability among individuals. An important characteristic of the fish is the length of the gill slit because it ultimately determines how much water can pass through the gills. The anterior edge of a gill slit is motile, moving outward to allow water to exit, but closing to prevent reverse flow. For Gulf killifish, their gill slit extends dorsal to the uppermost pectoral fin ray. In all, the Gulf killifish is one of the largest killifish species to have a blunt head and short snout.
The Gulf killifish can survive in wide ranges of habitats because it is highly adaptive. These adaptions have changed over time through evolution, which have allowed for the increased survival of the Gulf killifish. These different habitats include estuarine, lowland, upland, coastal marshes, lagoons, rivers, and streams. However, the Gulf killifish spends the majority of the time around brackish water near coasts.
The Gulf killifish is found in the Atlantic Ocean, the Gulf of Mexico, and the Caribbean Sea, and over the Southeast United States Continental Shelf. The normal range of Gulf killifish is from Texas to the western coast of Florida and from the east coast of Florida to Cuba. These waters undergo several changes in water characteristics such as temperature, dissolved oxygen, and salinity, among many other variables that can have profound effects on the survival and abundance of the Gulf killifish.
Spending a lot of time near the coasts ensures that the Gulf killifish is able to survive various salinity ranges including fresh water because their habitats get influx of freshwater into the ecosystems normally. It is able to withstand salinity ranges from 0 to 76 ppt. However, threats to the survival of the Gulf killifish occur because of changes in salinity. Salinity has profound effects on the development and hatching of their eggs. One of the secondary effects of the Deepwater Horizon oil spill was the opening of industrial canals to send fresh water into the Gulf to push the oil away from the marshes of Louisiana. This caused the salinity to drop quickly within some of the fish's habitat, which caused problems that had not been expected. One of these was that many eggs remained unhatched because the salinity levels had dropped below the critical salinity level where hatching can still occur. Another study looked into how salinity affects the survival and body size of fish within different salinities. The results from this study showed that the fish brought up in the lower salinity were less likely to survive, as well as have much lower body size and growth. These studies showed the importance of salinity on the survival of the Gulf killifish.
The normal climate for the Gulf killifish is tropical, as would be expected from where the fish is usually found. However, the Gulf killifish is able to survive in temperatures ranging from 5 to 37 °C. Temperature plays an important role in the hatching of viable eggs, as well as the relative abundance of these eggs. Lower water temperature with the use of shade in June, July, and August lead to the highest number and most viable eggs. However, in September, when the water temperature has begun to drop, the extra shading leads to much lower temperatures that lead to significantly fewer and less viable eggs. This study, as well as many like it, has shown that temperature can have profound effects on the overall survival of the Gulf killifish.
Another key characteristic of the habitats, which is influential to the survival of Gulf killifish, is the amount of dissolved oxygen. Fish need oxygen to survive and carry out normal activities and processes. Lower levels of oxygen is common in near-shore environments, one of the main habitats of the Gulf killifish. These conditions may last from several hours to several days. Gulf killifish use different ways to cope with low oxygen conditions, including behavioral changes, physiological changes, and changes to biochemical processes. One main threat because it decreases the levels of dissolved oxygen is the Louisiana dead zone, which causes a large number of fish killed every year. This dead zone results from nutrient- and chemical-rich water from the Mississippi River Valley basin entering the Gulf of Mexico. This eutrophic water ultimately leads to no dissolved oxygen remaining within the ecosystem because of increased activities of algae and decomposers. Therefore, the fish that remain will end up dying because of the lack of oxygen. Fish collected during the summer were better suited to hypoxic conditions because they were already acclimated to the lower levels of dissolved oxygen more so then than any other season. Due to the higher temperatures during the summer, less dissolved oxygen is available within the ecosystem.
Gulf killifish larvae
F. grandis is an egg-laying fish, and uses the soft muddy bottoms of saltwater or brackish ecosystems to lay eggs. They are known as an "annual" fish because their lifecycle, from birth to mating and ultimately death usually does not exceed one year. One adaptation that has allowed F. grandis to survive so efficiently is the versatile nature of their eggs. The eggs not only protect the developing embryo, but also prevents them from drying out and hindering the development of the inlaid fish. The egg's shell is sensitive to dissolved oxygen and carbon dioxide present within the water that can initiate hatching. This internal form of evolution is compromised when anthropomorphic effects disrupt the aquatic ecology in which they are laid.
Such biochemical effects may result from the presence of oil or oil dispersants in the water in which the fish lay their eggs. Time of exposure and the weather conditions present when the eggs are laid also play a definitive role in how these eggs and larvae can be affected. Oil or oil dispersants can become a hazard for larval F. grandis when they percolate down into the sediment where the eggs are laid. These substances can then begin to affect the biochemical morphology of the developing embryos or newly hatched larvae, leading to underdeveloped cardiovascular systems, decreased nerve functions, decreased endocrine and hormone secretions, and reduced gill tissue development.
Gulf killifish adults
F. grandis reaches adulthood as early as three to four months old, but on average close to 1 year of age. It may grow to about 6-7 in long when fully grown. Females may also grow 5–8 cm larger than the males and may exhibit more aggressive behaviors during the mating season. Once fully grown, F. grandis adults are omnivorous, feeding on algae and vascular plants, small grass shrimps (Palaemonetes), microcrustaceans (copepods), and mosquito larvae. Adults feed mainly on mosquito larvae and pupae, which has helped to reduce the mosquito population in marsh and wetland areas. F. grandis also serves as one of the most popular bait minnows for commercial and recreational fishing.
Deepwater Horizon oil spill
The Gulf killifish plays an important role in scientific research concerning the disaster resulting from the Deepwater Horizon oil spill. The spill occurred in April 2010 and resulted in an estimated 53,000 barrels per day of Macondo-252 crude oil being spilled from the well before it was capped in September 2010. The spill affected the Gulf coast area about a year and was finally determined to be maintained in October 2011. Several coastal reconstruction projects are still underway to try to restore the ecosystems of the Gulf.
Macondo-252 crude oil
The response of F. grandis fish to Macondo-252 crude oil depends mostly upon the stage in their lifecycle and their exposure time. Once spilled into water, this oil floats on the surface and affects F. grandis populations. The oil has the ability to harm fish species by different means. Floating oil can come into contact with the Gulf killifish by simply drifting into them, or the fish swimming through the oil trying to reach the surface. During the Deepwater Horizon spill, the Macondo-252 oil slick was composed of over 205 million gallons of crude oil. The floating oil affected the fish's health by being absorbed through the gills and getting into the eyes of the fish that came into contact with the oil. This imposed several physiological strains on them.
Macondo-252 oil may also drop within the water column and pose a new ecological threat, due to the oil percolating into the sedimentary layer under the water. The direct impacts are to the egg development and larval stage of the Gulf killifish. Oil in the sedimentary layer can be transferred through endocytosis-like processes that bring the developing F. grandis embryos into direct contact with the oil.
The toxicology of the oil dispersant Corexit 9500 on F. grandis has been studied. It is produced and distributed through NALCO and is a hazy, amber-colored liquid that acts to break down the oil. Corexit 9500 is sprayed by airplanes on floating oil slicks to cause the floating oil to sink to the bottom of the water in which it is suspended. Corexit 9500 was the primary oil dispersant used in the Deepwater Horizon oil spill in the Gulf, and impacted several of the Gulf coast aquatic ecosystems. The dispersant has been shown to affect biochemical pathways of some marine species, such as the Gulf kilifish.
The oil, after it sinks, causes several threats to the fish that use these soft, muddy bottoms for laying their eggs and larval development. The dispersant can also be poisonous to adults that come into contact with the floating dispersant within the water column. Being a hydrocarbon, the dispersant can be transferred into the cells of the fish if it is able to come into contact with internal structures through its mouth, eyes, anus, or any cuts or abrasions the fish may have. Once inside, poisoning can occur, causing the fish to physically deteriorate and become more susceptible to outside predation and any other natural elements with which they live.
- Ross, S.T. (2001). The Inland Fishes of Mississippi. University Press of Mississippi, Jackson. p. 624.
- Boschung, H.T.; R. L Mayden (2004). Fishes of Alabama. Washington: Smithsonian Books. p. 736.
- Lee, D.S.; C. R. Gilbert, C. H. Hocutt, R. E. Jenkins, D. E. McAllister, and J. R. Stauffer, Jr. (1980). Atlas of North American freshwater fishes. Raleigh, NC: North Carolina State Museum of Natural History.
- Simpson, D.G.; G. Gunter (1956). "Notes on habitats, systematic characters and life histories of Texas salt water cyprinodonts.". Tulane Stud. Zool. 4 (4): 115–134.
- Relyea, K (1983). "A systematic study of two species complexes of the genus Fundulus (Pisces: Cyprinodontidae)". Biol.Sci. 29 (1): 1–64.
- Hubbs, C.L.; R.J. Edwards and G.P. Garrett (1991). "An annotated checklist of freshwater fishes of Texas, with key to identification of species.". Texas Journal of Science 43 (4): 1–56.
- Smith, C.L. (1997). National Audubon Society field guide to tropical marine fishes of the Caribbean, the Gulf of Mexico, Florida, the Bahamas, and Bermuda. Alfred A. Knopf, Inc., New York. p. 720.
- Robins, C.R.; G.C. Ray ,and J. Douglass (1986). A field guide to Atlantic Coast fishes of North America. Houghton Mifflin Company, Boston, MA.
- Hubbs, C.; R.J. Edwards and G.P. Garrett (2008). "An annotated checklist of freshwater fishes of Texas, with key to identification of species.". Texas Journal of Science 43 (4): 1–87.
- Stevenson, H.M. (1976). Vertebrates of Florida. University Presses of Florida, Gainesville. p. 607.
- Wilson, Jonathan M.; Pierre Laurent (2002). Journal of Experimental Zoology 293 (3): 192–213. doi:10.1002/jez.10124.
- Connor, J.V.; R.D. Suttkus (1986). The Zoogeography of North American Freshwater Fishes. New York, New York: John Wiley and Sons. p. 866.
- G. H. Burgess (1980). "Fundulis grandis". In Lee, D. S. Atlas of North American Freshwater fishes. Raleigh, NC: N.C. State Mus. Nat. Hist. p. 516.
- Crego, G.J.; M.S. Peterson (1997). "alinity tolerance of four ecologically distinct species of Fundulus (Pisces: Fundulidae) from the northern Gulf of Mexico.". Gulf of Mexico Science: 45–49.
- Patterson, Joshua; Charlotte Bodinier; Christopher Green (2012). "Effects of low salinity media on growth, condition, and gill ion transporter expression in juvenile Gulf killifish, Fundulus grandis". Comparative Biochemistry and Physiology Part A: Molecular & Integrative Physiology 161 (4): 415–421. doi:10.1016/j.cbpa.2011.12.019.
- Brown, Charles A.; Craig T. Gothreaux; Christopher C. Green (2011). "Effects of temperature and salinity during incubation on hatching and yolk utilization of Gulf killifish Fundulus grandis embryos". Aquaculture 315 (3-4): 335–339. doi:10.1016/j.aquaculture.2011.02.041.
- Gothreaux, C.T.; C.C. Green (2012). "Effects of Shading on the Reproductive Output and Embryo Viability of Gulf Killifish". North American Journal of Aquaculture 74 (2): 266–272. doi:10.1080/15222055.2012.672368.
- Love, Joseph W.; Bernard B. Rees (2001). "Seasonal Differences in Hypoxia Tolerance in Gulf Killifish, Fundulus Grandis (Fundulidae)". Environmental Biology of Fishes 63 (1): 103–115.
- Tyson, R.V.; T.H. Pearson (1991). "Modern and ancient continental shelf anoxia: an overview". The Geological Society.
- Malone, T.C.; L.H. Crocker, S.E. Pike, B.W. Wendler (1988). "Influences of river flow on the dynamics of phytoplankton production in a partially stratified estuary". Marine Ecology Progress Series 48: 235–249. doi:10.3354/meps048235.
- "Killifish". Encyclopedia Britannica. Retrieved 21 October 2012.
- Lepley, Max. "Killifish Lifecycle". Infolific. Retrieved 22 October 2012.
- Thomas, Bonner, Whiteside. "Gulf Killifish Fundulus Grandis". Retrieved 22 October 2012.
- Dubansky B, Bodinier C, Rice CD, Whitehead A, Galvez F. "Effects of exposure to crude oil from the Deepwater Horizon Oil Spill on populations of Gulf killifish (Fundulus grandis) in Barataria Bay, Louisiana". Integrative and Comparative Biology 52 (Suppl 1). doi:10.1093/icb/ics078.
- Simpson, D. G. and G. Gunter (1956). "Notes on habitats, systematic characters and life histories of Texas salt water cyprinodonts". Tulane Stud. Zool 4 (4): 115–134.
- Harrington, R. W., Jr. and E. S. Harrington (1961). "Food selection among fishes invading a high subtropical salt marsh: from onset of flooding through the progress of a mosquito brood". Ecology 42 (4): 646–666. doi:10.2307/1933496.
- Robertson; Clifford, Campbell; Krauss. "Gulf Spill Is the Largest of Its Kind, Scientists Say". The NewYork Times.
- "Restore The Gulf". Retrieved 23 October 2012.
- Guarino, Mark. "Mystery in Gulf of Mexico: Why is oil leaking from Deepwater disaster site?". The Christian Science Monitor. Retrieved 24 October 2012.
- Gaskill, Melissa. "Trace amounts of crude oil harm fish". Deepwater Horizon spill affected gene expression in Gulf killifish. Nature.
- Whitty, Julia (1 September 2011). "Gulf Fish Hammered by BP Oil". Mother Jones. Retrieved 22 October 2012.
- eHow Contributo. "How Do Oil Spills Affect Fish?". Environmental Factors. http://www.how.com/howdoes_5489780_do-oil-spills-affect-fish.html.
- "Product Safety Department". Corexit 9500. Nalco. N. P. Retrieved 22 October 2012.
- Dubansky, Galvez, Green, Ben, Fernando, Christopher. "Embryonic Developments and metabolic costs in the Gulf killifish Fundulus grandis exposed to varying environmental salinities". Fish Physiology and Biochemistry 38 (4).
- Jamail, Dahr. "Oil and Dispersants: Huge Fish Kill at the Mouth of the Mississippi River". Global Research. Retrieved 7 November 2012.
Names and Taxonomy
Comments: Two subspecies: grandis and saguanus. The genus Fundulus was removed from Atheriniformes:Cyprinodontidae and placed in Cyprinodontiformes:Fundulidae by Parenti (1981); pending confirmation based on other character suites, this change was not accepted in the 1991 AFS checklist (Robins et al. 1991). See Wiley (1986) for a study of the evolutionary relationships of Fundulus topminnows based on morphological characters. See Cashner et al. (1992) for an allozyme-based phylogenetic analysis of the genus Fundulus.
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