Mottled sculpin

Mottled sculpin
Mottled sculpin (Cottus bairdii)
Scientific classification
Kingdom:	Animalia
Phylum:	Chordata
Class:	Actinopterygii
Order:	Scorpaeniformes
Family:	Cottidae
Genus:	Cottus
Species:	C. bairdii
Binomial name
Cottus bairdii Girard, 1850

The mottled sculpin, Cottus bairdii, is a freshwater sculpin (family Cottidae) found widely although unevenly throughout North America.

As the name suggests, its coloration is a combination of bars, spots, and speckles randomly distributed. The large pectoral fins are banded. The first dorsal fin is made of slender and somewhat soft spines, and just barely joins with the second dorsal. Maximum length is 15 cm.

It feeds primarily on aquatic insect larvae, but will also eat crustaceans, small fish, fish eggs, and some plant material. In turn, the sculpin is preyed upon by other fish, notably trout. Favored habitat is well-oxygenated and clear water, such as over gravel riffles in mountain streams, springs, and along rocky lake shores.

Spawning takes place during early winter and late spring. The male's head becomes darker, and he selects a protected nest site, such as under a rock or ledge. After courtship, the female enters the nest, turns upside down, and deposits her eggs on the ceiling, where they adhere. Typically several females will deposit eggs in a nest, then the male fertilizes and guards them, fanning the eggs with his pectoral fins.

Mottled sculpin occurrence is discontinuous in its range. It is widespread from the Tennessee River north to Labrador, while separate populations are found in the Missouri River, the Columbia River system in southern Canada, and the Bonneville system of the Great Basin.

Introduction

Mottled sculpins, Cottus bairdi, are a common fish throughout most of North America. The only area that mottled sculpin are provided limited protection is in New Mexico. ^[1] Mottled sculpins feed on a wide variety of organisms, including mollusks, snails, other mottled sculpins, and trout. Their diets are mainly made up of bottom-dwelling benthic insects.^[2] The favored habitat of a mottled sculpin is one rich in macroinvertebrate prey, which usually occurs in fast riffle areas^[3] with clear substrates and moderate velocities between 0.20m/s to 0.38m/s.^[4] Spawning season for the mottled sculpin starts in April or May ^[5] with the males taking up residency in benthic rocks. Breeding season lasts for two to three months.^[6] Clutch size can vary anywhere from 8 eggs to 148 eggs for females. Males can have up to 1587 eggs in their nest. Sexual maturity is thought to be reached at two years of age. Climate change does not seem to be a threat to this species since they inhabit a wide range of temperature gradient throughout the United States. However, one human activity that affects them is runoff from mining, which particularly is harmful to the newly hatched larvae and developing eggs.^[7] Nothing is being done for current management for the mottled sculpin because it is a very abundant fish where it occurs. Future management could focus on the different metals that leak into the water from mining. The absence of the mottled sculpin from an area could tell us that the area has high levels of zinc, cadmium, or copper.^[7]

Geographic distribution of species

The mottled sculpin, Cottus bairdi, is known to inhabit a large geographical range in North America. Their natural habitat range is from Northern Canada down to the Mobile and Tennessee River drainage systems. They are also commonly found in streams in the Rocky Mountains along with many steams found throughout the Midwest United States. The mottled sculpin has historically been found throughout all the environments listed above. For the most part, the geographical range of the mottled sculpin has not changed throughout the years due to it is being a resilient fish and because it has a large temperature gradient in which it can reside. However in a study by Besser and others in 2007, mottled sculpins have been absent in streams thought to be populated by them in the past due to the species being more sensitive to toxic levels of cadmium, copper, and zinc than species of salmonids.^[7] Of these three metals zinc seems to be the most threatening to the mottled sculpin. One study found mottled sculpins to be the third most sensitive aquatic species to zinc. ^[8]Therefore the biggest threat to the species would be high mining areas or areas where coal is burned frequently.

Ecology

Mottled sculpins are known for living in fast moving current areas where they feed primarily on bottom dwelling aquatic insects. One study found that bottom dwelling aquatic insects make up 99.7% of the mottled sculpin’s diet, with dipterous larvae and pupae being the most common type found.^[2] The remaining 0.3% was made up of snails, fingernail clams, water mites, sculpin eggs and fish.^[2] Thus the mottled sculpin is not a major threat to game fish though it has been found to eat trout eggs.^[2][9] Sculpin are cannibalistic. Males are known to eat their young if one contracts some kind of virus or fungus. The males also eat small females. Therefore older females are usually chosen for mates over younger females.^{[2] [5]} The main predators of the sculpin are different species of game fish, such as brook trout, brown trout, northern pike, and smallmouth bass. All sculpin species are expected to coexist with species from the Salmonidae family.^[9] Its main competitors are other small bottom dwelling fish, especially other sculpin species .^[4] Female and immature mottled sculpins are commonly found in clean water rock substrates. On the other hand, males are commonly found in algae beds. The mean current velocity in which the fish is found is 0.28 m/sec. They prefer to inhabit cool clear streams. They will tolerate warmer streams but do not prefer them like Cottus girardi.^[4]

Life history

Mottled sculpin reach sexual maturity at the age of two. ^[10] The breeding season for mottled sculpin is during April and May.^[5] At the beginning of the season the males will take refuge under flat-bottomed rocks, waterlogged wood or other rubble found in stream beds. In order to mate the female will come up to the males nest and lay her eggs there. The female chooses her mate on physical attributes. Since larger males pick out nesting sites with better resources qualities, the female’s choice of the largest male indicates she is picking good genes in a mate and also a good environment for her young to grow up^[11] After mating she either leaves or is chased away by the male. The males do this because females will eat the eggs right after spawning if the male does not run her off.^[12] The males continue to protect the eggs until they have absorbed their yolk sac and are ready to distribute themselves.^[13]

Mottled sculpins only mate once a year. The clutch size can vary anywhere from 8 eggs to 148 eggs for females. However within that year one male could mate with ten or more females^[11] This leads to very large nest sizes. One study looked at twelve different nesting sites within a year and found that one nest can have anywhere from 54 to 1587 eggs with an average of 744 eggs per nest.^[2] Mottled sculpin’s average life span is to age six.

Current management

The mottled sculpin is currently not federal or state listed for being threatened or endangered. In New Mexico the species is given limited protection. The reason for the species receiving no current management plan is due to its high abundance all over North America. Its high prevalence is due the species tolerance for all types of environment.

Although the species is not threatened anywhere in North America, it has received attention in recent areas in the Western United States due to its absence in some streams that are highly populated with trout species but not sculpins. This was odd since the two species usually coexist in similar habitats. The problem was that the streams absent of sculpin had high concentrations of zinc.^[8] One study showed that mottled sculpin are the third most sensitive species to high levels of zinc.^[8] The reason this occurring is because the U.S. Environmental Protection Agency (EPA) uses trout species to determine the water quality criteria (WQC) for zinc. ^[14] Therefore the WQC standards are not good enough to protect all species of fish. In southeast Minnesota there are plans to rebuild the sculpin population in streams where the water quality was once unfavorable for the species but has since been improved. The next step is to introduce 200 mottled sculpin a year until the population is showing signs of a comeback in the local streams.

However zinc is not the only metal threatening mottled sculpin populations. One study found mottled sculpins were also more sensitive to levels of copper and cadmium than other species of fish .^[7] The leading causes of increase of these three metals into aquatic environments are from mining, the burning of coal, steel production, and smelting metals. Other causes could be from accidents like the coal ash spill in Kingston, Tennessee in 2008.

Management recommendations

Although mottled sculpin are not a highly endangered fish, they are more sensitive than other fish to levels of copper, cadmium, and especially zinc in streams across North America. Therefore the absence of different sculpin species, especially mottled sculpin, in streams where other species of fish, such as trout, are abundant could be an indication of future trouble for these areas. Mottled sculpin could be used as an index species for the water quality in streams and rivers.

One thing that could be done to help the mottled sculpin return to its native western streams is for the EPA to use the mottled sculpin to set the WQCs for zinc. Once the new levels are set for the United States and zinc concentrations become more favorable for the species, the species can be reintroduced to these streams and hopefully reestablish populations once lost. One area that would be ideal for this project would be the segment of Eagle River downstream of an old mining area near Minturn, Colorado.^[14] This area would be ideal because it is a natural experiment. Up stream of the mining area mottle sculpin and brown trout are present, but directly downstream of the old mining town mottled sculpins are absent while brown trout have increased in numbers. Therefore it could be a goal to reduce the levels of zinc in the water downstream so that either a new population of mottled sculpins could be introduced or so that the upstream population could migrate downstream and have a larger population over all. If this were to work then it could be a guide line for further management plans for mottled sculpin.

References

• "Cottus bairdii". Integrated Taxonomic Information System. http://www.itis.gov/servlet/SingleRpt/SingleRpt?search_topic=TSN&search_value=167237. Retrieved 18 April 2006. 
• William F. Sigler and John W. Sigler, Fishes of the Great Basin (Reno: University of Nevada Press, 1987), pp. 348-350
• Froese, Rainer, and Daniel Pauly, eds. (2006). "Cottus bairdii" in FishBase. March 2006 version.

1. ^ http://www.fs.fed.us/rm/boise/AWAE/projects/fish_cattle/Mottled%20sculpin.pdf
2. ^ ^{a b c d e f} Bailey, JE. 1952. Life history and ecology of the sculpin “Cottus bardi punctulatus” in southwerstern Montana. Copeia 1952(4): 243-255.
3. ^ Rashleigh, B, GD Grossman. 2005. An individual-based simulation model for mottled sculpin (“Cottu bairdi”) in a southern Appalachian stream. Ecogological modeling 187: 247-258.
4. ^ ^{a b c} Matheson, RE, GR Brooks. 1983. Habitat segregation between “Cottus bairdi” and “Cottus girardi”:an example of complex inter- and intraspecific resource partitioning. American Midland Naturalist 110(1): 165-176.
5. ^ ^{a b c} Downhower, JF, L Brown, R Pederson, G Staples. 1983. Sexual selection and sexual dimorphism in mottled sculpins. Evolution 37(1):96-103.
6. ^ Downhower, JF, LS Blumer. 1987. Seasonal variation in sexual selection in the mottle sculpin. Evolution 41(6): 1386-1394.
7. ^ ^{a b c d} Besser, JM, CA Mebane, DR Mount, CD Ivey, JL Kunz. 2007. Sensitivity of mottled sculpin (“Cottus bairdi”) and rainbow trout (“Onchorhynchus mykiss”) to acute and chronic toxicity of cadmium, copper, and zinc. Environmental Toxicology and Chemistry 26(8): 1657-1665.
8. ^ ^{a b c} Brinkman, S., and J. Woodling. 2005. Zinc toxicity to the mottled sculpin (“Cottus bairdi”) in high-hardness water. Environmental Toxicology and Chemistry 24:1515-1517.
9. ^ ^{a b} Dineen, C. F. 1951. A comparative study of the food habitats of “Cottus bairdii and associated species of Salmonidae. American Midland Naturalist 46:640-645.
10. ^ Hann, H.W. 1927. The history of the germ cells of “Cottus bairdi” Girard. Journal of Morphology and Physiology 43:427-497 .
11. ^ ^{a b} Downhower, J.F., and L. Brown. 1980. Mate preference of female mottled sculpins “Cottus bairdi”.
12. ^ Savage, T. 1963. Reproductive behavior of the mottled sculpin, “Cottus bairdi” Girard. Copeia 1963:317-325.
13. ^ Downhower, J.F., and R. Yost. The significance of male parental care in the mottled sculpin, “Cottus bairdi”. American Zoology 17:936.
14. ^ ^{a b} Woodling, J., S. Brinkman, and S. Albeke. 2002. Acute and chronic toxicity f zinc to the mottled sculpin “Cottus bairdi”