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Overview

Brief Summary

Notes

Holotype: not located, according to roze and Tilger, 1983, Cat. Am. Amph. Rept. 316:1-4[1].

Type-locality: Carolina. Restricted to vicinity of Chareston, South Carolina, USA, by Schmidt, 1953, Check List n. Am. Amph. Rept., 6th ed., 280 pp.[223].

Five subspecies, namely M. f. fulvius (Linnaeus, 1766); M. f. fitzingeri (Jan, 1858); M. f. maculatus Roze, 1967; M. f. microgalbineus Brown and Smith, 1942; and M. f. tener (Baird and Girard, 1853), were recognized by Roze and Tilger, 1983, Cat. Am. Amph. Rept. 316:1-4.

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Distribution

Range Description

This species occurs in the south of the United States, extending into northeastern Mexico. It ranges from southeastern North Carolina to southern Florida, west to southeastern Louisiana, disjunctly northward to central Alabama (Ashton and Ashton 1981, Mount 1975, Dundee and Rossman 1989, Palmer and Braswell 1995, Tennant 1997, Campbell and Lamar 2004).
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Geographic Range

There are five subspecies. M. f. fulvius occurs in southeast N. Carolina south through Florida and west to Louisiana. The other four range from western Louisiana southwest through southern Texas to eastern & central Mexico (Barbour & Earnst 1989).

Biogeographic Regions: nearctic (Native )

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endemic to a single nation

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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: (200,000-2,500,000 square km (about 80,000-1,000,000 square miles)) Southeastern North Carolina to southern Florida, west to southeastern Louisiana, disjunctly northward to central Alabama (Ashton and Ashton 1981, Mount 1975, Dundee and Rossman 1989, Palmer and Braswell 1995, Tennant 1997, Campbell and Lamar 2004).

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Continent: North-America
Distribution: USA (S/C/E Texas, Louisiana, S Arkansas, Mississippi, Alabama, Georgia, Florida, South Carolina, SE North Carolina).
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Distribution

Southeastern USA from southeastern north Carolina through peninsular Florida westward to eastern and west-central Texas (apparently absent from the delta region of the lower Mississippi Valley), and southward into northeastern and central Mexico, including portions of the states of Tamaulipas, Nuevo León, Coahuila, Querétaro, San Luis Potosí, Hidalgo, Guanajuato, and morelos.

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Physical Description

Morphology

Physical Description

Banded with red, white, or yellow and black on which the red and yellow bands lie beside each other, and the snout is black. Size ranges from two-three feet (Barket 1964). The body scales are smooth and occur in 15 rows throughout; the anal plate is divided.

Confusing species: several subspecies of Lampropeltis triangulum and the species Cemophora coccinea also have red, yellow and black bands crossing their bodies, but their red and yellow bands are separated by black bands and their snouts are red instead of black (Barbour & Ernst 1989).

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Size

Length: 121 cm

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
Habitats include hardwood forest, pine-oak woodland, pine flatwoods, and xerophytic scrub, often in areas with sandy soils, sometimes marsh edges and residential areas (Mount 1975, Ashton and Ashton 1981, Palmer and Braswell 1995, Tennant 1997, Ernst and Ernst 2003). This secretive snake is often underground, under leaf litter, logs or stumps, or similarly secluded. Eggs probably are laid in loose soil or decaying organic matter (Mount 1975), or underground or under leaf litter or surface objects (Ernst 1992).

Systems
  • Terrestrial
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Habitat

M. fluvius spends most of the time buried in the soil, in forest areas among decaying logs, leaves, and rocks. It seems to prefer dry, open or brushy areas, occasionally in marshy areas (Conant & Collins 1991).

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Comments: Habitats include hardwood forest, pine-oak woodland, pine flatwoods, and xerophytic scrub, often in areas with sandy soils, sometimes marsh edges and residential areas (Mount 1975, Ashton and Ashton 1981, Palmer and Braswell 1995, Tennant 1997, Ernst and Ernst 2003). This secretive snake is often underground, under leaf litter, logs or stumps, or similarly secluded. Eggs probably are laid in loose soil or decaying organic matter (Mount 1975), or underground or under leaf litter or surface objects (Ernst 1992).

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Migration

Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.

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.

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Trophic Strategy

Food Habits

M. fulvius' diet consists mostly of snakes, including its own species. It also eats lizards, birds, frogs, fish, and insects. It uses venom to kill its victims (Stebbins 1966).

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Comments: Eats mainly snakes and limbless or small-limbed lizards (Jackson and Franz 1981, Ernst 1992); sometimes anurans and rodents.

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Associations

Known prey organisms

Micrurus fulvius preys on:
Thamnophis sirtalis
Diadophis punctatus

This list may not be complete but is based on published studies.
  • Myers, P., R. Espinosa, C. S. Parr, T. Jones, G. S. Hammond, and T. A. Dewey. 2006. The Animal Diversity Web (online). Accessed February 16, 2011 at http://animaldiversity.org. http://www.animaldiversity.org
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Population Biology

Number of Occurrences

Note: For many non-migratory species, occurrences are roughly equivalent to populations.

Estimated Number of Occurrences: 81 - 300

Comments: This species is represented by a large number of occurrences (subpopulations). On a range-wide scale, Campbell and Lamar (2004) mapped more than 100 collection sites.

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Global Abundance

100,000 - 1,000,000 individuals

Comments: Adult population size is unknown but presumably exceeds 100,000. Nearly 2,000 were turned in for bounties in a 39-month period in one county in Florida (see Ernst and Ernst 2003). This snake is often common; its secretive habits may give a false impression of rarity (Ernst 1992). Mount (1975) characterized it as relatively common in the lower Coastal Plain of Alabama. Tennant (1997) reported it as common in Florida.

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Life History and Behavior

Cyclicity

Comments: In the northern part of the range, active mainly in daytime; diurnal activity occurs principally during morning and late afternoon. Active all year in Florida, especially in spring and fall, least active in winter (Jackson and Franz 1981).

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Life Expectancy

Lifespan/Longevity

Average lifespan

Status: captivity:
6.8 years.

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Lifespan, longevity, and ageing

Maximum longevity: 19 years (captivity)
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Reproduction

Reproduction

M. fulvius breeds from late spring early summer and late summer to early fall. Eggs are laid during May to July. There are approximately 37 days between copulation and ovipostion. Clutches of 5-7 eggs will be laid and the young will hatch approximately 60 days later (Barket 1964, Stebbins 1966).

Females mature at a snout-vent length of about 55cm in 21-27 months. Males mature sexually usually around 45cm or longer reached in 11-21 months.

Ovary weights increase from March through April, and decline slightly in May and then more rapidly in June. There is complete regression with spermatogonia and Sertoli cells in May through August, with a peak in June (Barbour & Ernst 1989).

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Mating occurs in spring and possibly also in fall (Ernst 1992). Lays clutch of 2-13 (often 4-7) eggs, May or June to July; eggs hatch in late summer or fall, after about 10-13 weeks of incubation; males sexually mature in 11-21 months, females in about 21-27 months (Jackson and Franz 1981, Behler and King 1979, Ernst and Barbour 1989).

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2007

Assessor/s
Hammerson, G.A.

Reviewer/s
Cox, N., Chanson, J.S. & Stuart, S.N. (Global Reptile Assessment Coordinating Team)

Justification
Listed as Least Concern in view of its wide distribution, presumed large population, and because it is unlikely to be declining fast enough to qualify for listing in a more threatened category.
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Conservation Status

IUCN Red List of Threatened Species: least concern

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National NatureServe Conservation Status

United States

Rounded National Status Rank: N5 - Secure

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NatureServe Conservation Status

Rounded Global Status Rank: G5 - Secure

Reasons: Secure in fairly large range in the southeastern United Staes; even where fairly common may appear to be scarce due to secretive habits.

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Population

Population
This species is represented by a large number of occurrences (subpopulations). On a range-wide scale, Campbell and Lamar (2004) mapped more than 100 collection sites. The adult population size is unknown but presumably exceeds 100,000. Nearly 2,000 were turned in for bounties in a 39-month period in one county in Florida (see Ernst and Ernst 2003). This snake is often common; its secretive habits may give a false impression of rarity (Ernst 1992). Mount (1975) characterized it as relatively common in the lower Coastal Plain of Alabama. Tennant (1997) reported it as common in Florida. Population trends are not documented, but its extent of occurrence, area of occupancy, number of subpopulations, and populations size are probably relatively stable or declining at a rate of less than 10% over 10 years or three generations.

Population Trend
Stable
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Global Short Term Trend: Relatively stable (=10% change)

Comments: Trend is not documented, but extent of occurrence, area of occupancy, number of subpopulations, and populations size probably are relatively stable or declining at a rate of less than 10 percent over 10 years or three generations.

Global Long Term Trend: Increase of 10-25% to decline of 30%

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Threats

Threats

Major Threats
Overall, this species does not appear to be significantly threatened. In Alabama, populations declined after introduction of the fire ant, which may prey on eggs and young (Mount 1981). Habitat destruction and motorized vehicles are the most serious threats (Ernst 1992, Ernst and Ernst 2003).
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Comments: Overall, this species does not appear to be significantly threatened. In Alabama, populations declined after introduction of the fire ant, which may prey on eggs and young (Mount 1981). Habitat destruction and motorized vehicles are the most serious threats (Ernst 1992, Ernst and Ernst 2003).

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Management

Conservation Actions

Conservation Actions
Many occurrences are in protected areas.
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Global Protection: Many to very many (13 to >40) occurrences appropriately protected and managed

Comments: Many occurrences are in protected areas.

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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

Although it is not likely to be bitten by a wild coral snake, unless it is harassed, the venom is extremely toxic and can cause death.

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Economic Importance for Humans: Positive

Their neurotoxic venom is one of the venoms used in antiserum for snake bites. Venom is also being researched like many other venomous snakes. Research is being done for cancer, AIDS, and other disabilitating diseases. Without these animals for research we may lose many key cures.

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Economic Uses

Comments: Venomous but innocuous; humans are unlikely to be bitten unless intentionally handling the snake. See Ernst and Barbour (1989) and Ernst (1992) for information and references pertaining to envenomation of humans.

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Wikipedia

Micrurus fulvius

Common names: Eastern coral snake,[2] common coral snake, American cobra,[3] more.

Micrurus fulvius is a venomous elapid snake found in the southeastern United States and northeastern Mexico.[4] It should not be confused with the scarlet snake (Cemophora coccinea) or scarlet kingsnake (Lampropeltis triangulum elapsoides), which are harmless mimics.[2] No subspecies are currently recognized.[5]

Contents

Description

Coral snake.jpg

Generally less than 80 cm (31 in) in length, its maximum reported length of 121.8 cm (48.0 in) was for a specimen in Florida (Niell, 1958) and 129.5 cm (51.0 in) (Roze, 1996). Males have longer tails than females, but females reach a greater total length.[1]

The dorsal scales are smooth in 15 rows.[2] The ventral scales number 197-217 in males and 219-233 in females. There are 40-47 subcaudals in males and 30-37 in females.[1] The anal plate is divided.[2]

The color pattern consists of a series of rings that encircle the body: wide red and black rings separated by narrow yellow rings. The head is black from the rostral to just behind the eyes. The red rings are usually speckled with black.[2] People who live in its natural range are often taught a folk rhyme as children: "Red touches black, friend of Jack, red touches yellow, kill a fellow." The rhyme is useful in teaching children to distinguish king snakes (Lampropeltis ssp.), which are considered helpful predators of vermin such as rats and mice, from this much more dangerous snake that should only be handled by an experienced biologist or herpetologist.

Common names

Its common names include eastern coral snake,[2] American cobra, candy stick, common coral snake, coral adder, Elaps harlequin snake, Florida coral snake, harlequin coral snake, North American coral snake, red bead snake, thunder-and-lightning snake,[3] candy-stick snake, eastern coralsnake, Florida coralsnake, harlequin coralsnake,[1] and serpiente-coralillo arlequín (Spanish).[5]

Geographic range

This snake is found in the Southeastern United States from southeastern North Carolina, south through South Carolina and peninsular Florida, and westward through southern Georgia, Alabama and Mississippi to southeastern Louisiana. It may be found at altitudes of near sea level to about 400 m (1,300 ft).[1]

Habitat

M. fulvius occurs in upland mesophytic and tropical hammocks in Florida, as well as glade land, high pine, scrub oak and live oak hammock, slash pine and wiregrass flatwoods. In southern Georgia and Florida, it is found in dry areas with open ground that are bushy but not heavily vegetated. It is associated with sandy ridges in Mississippi and sandy creek bottoms in Louisiana.[1] It is rarer in North and South Carolina, but is more typically found there in the scrub oak forests and pitch pine habitats near the coast.

Feeding

They eat lizards, frogs and smaller snakes.[2][6]

Reproduction

Females are reported to lay 3-12 eggs in June that hatch in September. Neonates are 18–23 cm (7.1–9.1 in) in length.[2]

Venom

Only two documented fatalities were attributed to this species in the 1950s, and only one has been reported since Wyeth antivenin became available for it in the 1960s. The most recent fatality attributed to the eastern coral snake occurred in 2009.[7] The victim failed to seek proper medical attention and died several hours after being bitten, becoming the first fatality caused by M. fulvius in over 40 years.[7]

M. fulvius does not account for many cases of snakebite in the U.S., with only about 100 bites each year.[8] The snake is considered secretive and generally reluctant to bite (its venomous potential was still being debated in the 1880s), and envenomation is thought to occur in only 40% of all bites.[1] But unlike New World pit vipers, this New World coral snake cannot control the amount of primarily neurotoxic venom injected. Dry bites often result from a near miss or deflection; although the venom an adult coral snake holds is enough to kill up to five adults, it cannot release all its venom in a single bite.[9][10] Historically, however, the mortality rate was estimated to be about 10–20%, with death occurring in as little as one to two hours, or as much as 26 hours after the bite. This is not that surprising, since the LD100 for humans is estimated to be 4–5 mg of dried venom, while the average venom yield is 2–6 mg with a maximum of more than 12 mg. This is probably why current standard hospital procedure in the U.S. is to start with antivenin therapy for coral snake bites, even if there are no symptoms yet (since there may not be any noticeable, localized symptoms).[1]

Wyeth discontinued the manufacture of coral snake antivenin in 2010, citing a lack of profitability.[8]

References

  1. ^ a b c d e f g h Campbell JA, Lamar WW. 2004. The Venomous Reptiles of the Western Hemisphere. Comstock Publishing Associates, Ithaca and London. 870 pp. 1500 plates. ISBN 0-8014-4141-2.
  2. ^ a b c d e f g h Behler JL, King FW. 1979. The Audubon Society Field Guide to North American Reptiles and Amphibians. New York: Alfred A. Knopf. 743 pp. LCCCN 79-2217. ISBN 0-394-50824-6.
  3. ^ a b Wright AH, Wright AA. 1957. Handbook of Snakes. Comstock Publishing Associates. (7th printing, 1985). 1105 pp. ISBN 0-8014-0463-0.
  4. ^ Micrurus fulvius at the IUCN Red List. Accessed 05 August 2010.
  5. ^ a b "Micrurus fulvius". Integrated Taxonomic Information System. http://www.itis.gov/servlet/SingleRpt/SingleRpt?search_topic=TSN&search_value=174354. Retrieved 12 December 2006. 
  6. ^ http://animals.nationalgeographic.com/animals/reptiles/eastern-coral-snake.html
  7. ^ a b Norris, Robert L., Robert L.; Robert R. Pfalzgraf, Gavin Laing (March 2009). "Death following coral snake bite in the United States – First documented case (with ELISA confirmation of envenomation) in over 40 years". Toxicon 53 (6): 693–97. doi:10.1016/j.toxicon.2009.01.032. PMID 19673084. http://www.sciencedirect.com/science?_ob=ArticleURL&_udi=B6TCS-4VJ4WK95&_user=10&_rdoc=1&_fmt=&_orig=search&_sort=d&_docanchor=&view=c&_searchStrId=1061675458&_rerunOrigin=scholar.google&_acct=C000050221&_version=1&_urlVersion=0&_userid=10&md5=507bc0b374eeab8ca012e799e7a50b5f. 
  8. ^ a b Derene, Glenn (May 10, 2010). "Cost of Antivenom Production Creates Shortages". Popular Mechanics. http://www.popularmechanics.com/science/health/snakebites-about-to-get-more-deadly. Retrieved 19 February 2012. 
  9. ^ "Snake Bites". Survive Outdoors. http://www.surviveoutdoors.com/reference/snakes/snake-bites.asp/. Retrieved 2010-05-13. 
  10. ^ "Eastern Coral Snake Micrurus fulvius". National Geographic. http://animals.nationalgeographic.com/animals/reptiles/eastern-coral-snake.html/. Retrieved 2010-05-13. 
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Names and Taxonomy

Taxonomy

Comments: Micrurus tener formerly was included as a subspecies of M. fulvius. Crother et al. (2000), Collins and Taggart (2002), and Campbell and Lamar (2004) recognized M. tener and M. fulvius as distinct species.

Phylogenetic relationships of elapid snakes based on mtDNA data indicate that New World coralsnakes cluster with Asian coralsnakes (Slowinski and Keogh 2000).

See Slowinski (1995) for a phylogenetic analysis of New World coralsnakes.

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