{"elementGlobalId":105757,"circumscripConfidence":{"id":1,"circumscripConfidenceDescEn":"1 - Strong","circumscripConfidenceDescEs":"1 - Fuerte","circumscripConfidenceDescFr":"1 – Forte"},"classificationLevel":{"id":7,"classificationLevelNameEn":"Species","classificationLevelNameEs":"Especies","classificationLevelNameFr":"Espèce"},"classificationStatus":{"id":1,"classificationStatusDescEn":"Standard","classificationStatusDescEs":"Estándar","classificationStatusDescFr":"Standard"},"iucn":{"id":11,"iucnDescEn":"Least concern","iucnDescEs":"Menos preocupante","iucnDescFr":"Moins préoccupante","iucnCode":"LC"},"nameCategory":{"id":1,"nameCategoryDescEn":"Vertebrate Animal","nameCategoryDescEs":"Animal vertebrado","nameCategoryDescFr":"Animal vertébré","nameTypeCd":"A","nameTypeDesc":"Zoological"},"rankMethodUsed":null,"formattedScientificName":"<i>Nerodia cyclopion</i>","scientificName":"Nerodia cyclopion","scientificNameAuthor":"(Dumeril, Bibron, and Dumeril, 1854)","primaryCommonName":"Mississippi Green Watersnake","relatedItisNames":"<i>Nerodia cyclopion</i> (Duméril, Bibron and Duméril, 1854) (TSN 174243)","uniqueId":"ELEMENT_GLOBAL.2.105757","elcode":"ARADB22010","conceptRefFullCitation":"Lawson, R. 1987. Molecular studies of thamnophiine snakes: 1. The phylogeny of the genus <i>Nerodia</i>. J. Herpetology 21:140-157.","conceptName":"<i>Nerodia cyclopion</i>","taxonomicComments":"<i>Nerodia floridana</i> formerly was included in <i>N. cyclopion</i> (see Lawson 1987).","roundedGRank":"G5","conservationStatusFactorsEditionDate":"2006-09-02","conservationStatusFactorsEditionAuthors":"Hammerson, G.","primaryCommonNameLanguage":"EN","recordType":"SPECIES","elementNationals":[{"elementNationalId":165074,"classifConfidence":null,"nation":{"id":225,"nameEn":"United States","nameEs":"Estados Unidos","nameFr":"États-Unis","isoCode":"US","region":"United 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of <30% to increase of 25%","longTermTrendDescEs":"Disminución de <30% a aumento de 25%.","longTermTrendDescFr":"Diminution de <30 % à augmentation de 25 %"},"numberEos":{"id":14,"numberEosDescEn":"81 to >300","numberEosDescEs":"De 81 a >300","numberEosDescFr":"De 81 à >300"},"numberGoodEos":{"id":17,"numberGoodEosDescEn":"Some to many (13-125)","numberGoodEosDescEs":"Algunos a muchos (13-125)","numberGoodEosDescFr":"De quelques-uns à plusieurs (de 13 à 125)"},"numberProtEos":{"id":11,"numberProtEosDescEn":"Several to many (4-40) occurrences appropriately protected and managed","numberProtEosDescEs":"De unas pocas a varias ocurrencias (4 a 40) protegidas y debidamente controladas","numberProtEosDescFr":"De quelques à plusieurs occurrences (de 4 à 40) protégées et contrôlées convenablement"},"popSize":{"id":35,"popSizeDescEn":"100,000 to >1,000,000 individuals","popSizeDescEs":"De 100.000 a >1.000.000 de individuos","popSizeDescFr":"De 100 000 à >1 000 000 individus"},"rangeExtent":{"id":31,"rangeExtentDescEn":"20,000-2,500,000 square km (about 8000-1,000,000 square miles)","rangeExtentDescEs":"De 20.000 a 2.500.000 kilómetros cuadrados (aproximadamente 8.000 a 1.000.000 de millas cuadradas)","rangeExtentDescFr":"De 20 000 à 2 500 000 km carrés (de 8 000 à 1 000 000 miles carrés approximativement)"},"shortTermTrend":{"id":40,"shortTermTrendDescEn":"Relatively Stable (<=10% change)","shortTermTrendDescEs":"Relativamente estable (variación = <10%)","shortTermTrendDescFr":"Relativement stable (variation = <10 %)"},"threatImpactAssigned":{"id":8,"threatImpactAssignedDescEn":"Medium","threatImpactAssignedDescEs":"Medio","threatImpactAssignedDescFr":"Moyen"},"rangeExtentComments":"The range extends on the Coastal Plain from extreme western Florida and southern Alabama to southeastern Texas, and north in the Mississippi Valley to extreme southeastern Missouri and southern Illinois (Barbour 1971, Dundee and Rossman 1989, Conant and Collins 1991, Phillips et al. 1999, Johnson 2000, Werler and Dixon 2000, Ernst and Ernst 2003, Gibbons and Dorcas 2004, Trauth et al. 2004).","areaOfOccupancy":null,"areaOfOccupancyComments":null,"numberEosComments":"This species is represented by a large number of occurrences (subpopulations).  Most occurrences are in the southern part of the range (e.g., see dot maps in Dundee and Rossman 1989, Werler and Dixon 2000), with relatively few in the north (Barbour 1971, Phillips et al. 1999, Johnson 2000, Trauth et al. 2004). ","popSizeComments":"Adult population size is unknown but presumably exceeds 100,000. This snake is very common in some parts of the southern part of the range (Dundee and Rossman 1989), though uncommon in Texas (Tennant 1998, Werler and Dixon 2000). It is much less numerous northward in the Mississippi valley (Trauth et al. 2004), but even in the north some local populations may be fairly large (Keiser 1958).","viabilityComments":null,"threatImpactComments":"No major threats are known. Declines have occurred as a result of drainage of sloughs and swamps and removal of aquatic vegetation, particularly in the northern part of the range (Phillips et al. 1999, Johnson 2000, Ernst and Ernst 2003).","shortTermTrendComments":"Currently, extent of occurrence, area of occupancy, number of subpopulations, and population size probably are relatively stable or declining at a rate of less than 10 percent over 10 years or three generations.","longTermTrendComments":"This species seemingly was always relatively uncommon and sparsely distribued in the northern part of the range, where today it is even more so as a result of habitat loss. ","inventoryNeeds":null,"numberProtEosComments":"At least several occurrences are in protected areas.","protectionNeeds":null,"otherConsiderations":null,"intrinsicVulnerabilityComments":null,"enviromentalSpecificityComments":null},"animalCharacteristics":{"elementGlobalId":105757,"majorHabitat":{"id":3,"majorHabitatDescEn":"Terrestrial","majorHabitatDescEs":"Terrestre","majorHabitatDescFr":"Terrestre"},"nonMigrant":true,"localMigrant":false,"longDistanceMigrant":false,"mobilityMigrationComments":null,"foodHabitsComments":"Eats frogs, fishes, salamanders, tadpoles, small turtles, amd invertebrates (Ashton and Ashton 1981, Tennant 1984).","animalPhenologyComments":"Primarily diurnal in Illinois, almost exclusively nocturnal in Texas (Tennant 1984).","colonialBreeder":false,"length":127,"width":null,"weight":null,"animalPhenologies":[{"animalCagPhenologyId":102231,"animalPhenology":{"id":3,"animalPhenologyDescEn":"Diurnal","animalPhenologyDescEs":"Diurno","animalPhenologyDescFr":"Diurne","displayOrder":3},"adult":true,"immature":true},{"animalCagPhenologyId":102232,"animalPhenology":{"id":4,"animalPhenologyDescEn":"Nocturnal","animalPhenologyDescEs":"Nocturno","animalPhenologyDescFr":"Nocturne","displayOrder":4},"adult":true,"immature":true},{"animalCagPhenologyId":102233,"animalPhenology":{"id":5,"animalPhenologyDescEn":"Crepuscular","animalPhenologyDescEs":"Crepuscular","animalPhenologyDescFr":"Crépusculaire","displayOrder":5},"adult":true,"immature":true}],"animalFoodHabits":[{"animalCagFoodHabitsId":104170,"foodHabits":{"id":1,"foodHabitsDescEn":"Carnivore","foodHabitsDescEs":"Carnívoro","foodHabitsDescFr":"Carnivore","displayOrder":1},"adult":true,"immature":true},{"animalCagFoodHabitsId":104171,"foodHabits":{"id":2,"foodHabitsDescEn":"Piscivore","foodHabitsDescEs":"Piscivore","foodHabitsDescFr":"Piscivore","displayOrder":2},"adult":true,"immature":true}]},"occurrenceDelineations":[{"eoSpecsDetailId":1142,"locationUseClass":{"id":1,"locationUseClassDescEn":"Not applicable","locationUseClassDescEs":"No se aplica","locationUseClassDescFr":"Sans objet","displayOrder":1},"eoSpecGroupName":"Medium And Large Colubrid Snakes","subtypes":null,"inferredExtentDistance":0.5,"inferredExtentNotes":null,"minimumEoCriteria":"Occurrences are based on evidence of historical presence, or current and likely recurring presence, at a given location. Such evidence minimally includes collection or reliable observation and documentation of one or more individuals (including eggs) in or near appropriate habitat where the species is presumed to be established and  breeding.","mappingGuidance":null,"separationBarriers":"Busy highway or highway with obstructions such that snakes rarely if ever cross successfully; major river, lake, pond, or deep marsh (this barrier pertains only to upland species and does not apply to aquatic or wetland snakes); densely urbanized area dominated by buildings and pavement.","separationDistanceUnsuitableHabitatat":1.0,"separationDistanceSuitableHabitatat":10.0,"altSeparationProcedure":null,"separationJustification":"Available information on movements of colubrid snakes is limited to a small minority of species. These data indicate that nearly all species have home ranges smaller or much smaller than 25 ha (e.g., less than 3 ha, <i>Pituophis catenifer</i> in California, Rodriguez-Robles 2003), with some up to about 75 ha (<i>Heterodon platirhinos</i>, average 50 ha, Plummer and Mills 2000), and the largest up to 225 ha in the biggest colubrids (<i>Drymarchon</i>, summer mean 50-100 ha, USFWS 1998). <br><br>Radiotelemetry data for <i>Pantherophis </i>indicate that residents of hibernacula that are 1-2 km apart (with suitable intervening habitat) probably interbreed (Prior et al. 1997, Blouin-Demers and Weatherhead 2002). However, \"evidence of genetic structure even over short distances (e.g., 2-20 km) implies that gene flow among rat snake populations can be easily disrupted\" (Prior et al. 1997). Loughheed et al. (1999) found evidence of substantial genetic exchange among local hibernacula (< 6 km apart), but gene flow over distances of 10s of km appears to be substantially less. Based on extensive radio-tracking data, Blouin-Demers and Weatherhead (2002) found that home range size of <i>Pantherophis </i>averaged 18.5 ha and ranged up to 93 ha; based on the most mobile individuals, <i>Pantherophis </i>from hibernacula up to 8 km apart can come together for mating. <i>Pantherophis </i>and probably other colubrids exhibit high fidelity to hibernacula and shift even to nearby sites only rarely (Prior et al. 2001). <br><br>Many of the several studies that report small home ranges for colubrids did not employ methods (e.g., radio telemetry) suitable for detecting full annual or multi-annual home range size, dispersal, or other long-distance movements, so these may have yielded underestimates of home ranges or activity areas.  <br><br>At least some colubrids, including medium-sized species such as garter snakes, not uncommonly move between areas up to a few kilometers apart, and several species make extensive movements of up to several kilometers, so separation distances of 1-2 km for suitable habitat are too small for medium-sized and large colubrids.<br><br>A separation distance of 10 km for suitable habitat was selected as most appropriate for snakes assigned to this Specs Group because it seems generally unlikely that two locations separated by less than 10 km of suitable habitat would represent distinct occurrences.<br><br>For the purposes of these occurrence specifications, upland habitat is regarded as unsuitable habitat for aquatic and wetland snakes. For upland snakes, shallow or patchy wetlands are treated as unsuitable habitat whereas large deepwater habitats (subjective determination) are barriers.","versionDate":"2013-02-12","versionAuthor":"Hammerson, G.","versionNotes":"Separation distance for suitable habitat was changed from 5 km to 10 km based on comments from Dale Jackson (12 Feb 2013).","lastModified":"2020-04-30T02:04:05.987846Z"}],"plantCharacteristics":null,"elementManagement":{"elementGlobalId":105757,"eoManagementGroupName":null,"stewardshipOverview":null,"impacts":null,"restorationPotential":null,"siteConservationPlansConsidered":null,"managementMethods":null,"monitoringMethods":null,"managementProgramContacts":null,"monitoringProgramContacts":null,"managementResearchPrograms":null,"managementResearchNeeds":null,"biologicalResearchNeeds":null,"additionalTopics":null},"occurrenceViabilities":[{"eoRankSpecsDetailId":107176,"eoRankSpecsGroupName":null,"locationUseClass":{"id":1,"locationUseClassDescEn":"Not applicable","locationUseClassDescEs":"No se aplica","locationUseClassDescFr":"Sans objet","displayOrder":1},"excellentViability":null,"goodViability":null,"fairViability":null,"poorViability":null,"viabilityJustification":"Use the Generic Guidelines for the Application of Occurrence Ranks (2008).<br>The Key for Ranking Species Occurrences Using the Generic Approach provides a step-wise process for implementing this method.","versionDate":null,"versionAuthor":null,"versionNotes":null,"lastModified":"2020-05-14T02:29:46.778409Z"}],"references":[{"id":100882,"citation":"Ashton, R. E., Jr., and P. S. Ashton. 1981. Handbook of reptiles and amphibians of Florida. Part One: The Snakes. Windward Publishing Company, Miami, Florida. 176 pp.","shortCitationAuthor":"Ashton and Ashton","shortCitationYear":1981,"referenceCode":"B81ASH01NAUS","lastModified":"2020-02-25T18:12:09.428867Z"},{"id":134853,"citation":"Barbour, R. W. 1971. Amphibians and reptiles of Kentucky. Univ. Press of Kentucky, Lexington. x + 334 pp.","shortCitationAuthor":"Barbour","shortCitationYear":1971,"referenceCode":"B71BAR01NAUS","lastModified":"2020-02-25T18:11:59.913087Z"},{"id":137372,"citation":"Behler, J. L., and F. W. King. 1979. The Audubon Society field guide to North American reptiles and amphibians. Alfred A. Knopf, New York. 719 pp.","shortCitationAuthor":"Behler and King","shortCitationYear":1979,"referenceCode":"B79BEH01NAUS","lastModified":"2020-02-25T14:38:24.173666Z"},{"id":137880,"citation":"Collins, J. T. 1990. Standard common and current scientific names for North American amphibians and reptiles. 3rd ed. Society for the Study of Amphibians and Reptiles. Herpetological Circular No. 19. 41 pp.","shortCitationAuthor":"Collins","shortCitationYear":1990,"referenceCode":"B90COL01NAUS","lastModified":"2020-02-25T14:38:15.579798Z"},{"id":104608,"citation":"Conant, R. and J. T. Collins. 1991. A field guide to reptiles and amphibians: eastern and central North America. Third edition. Houghton Mifflin Co., Boston, Massachusetts. 450 pp.","shortCitationAuthor":"Conant and Collins","shortCitationYear":1991,"referenceCode":"B91CON01NAUS","lastModified":"2020-02-25T18:11:51.303794Z"},{"id":140525,"citation":"Conant, R., and J. T. Collins. 1998. A field guide to reptiles and amphibians: eastern and central North America. Third edition, expanded. Houghton Mifflin Co., Boston, Massachusetts. 616 pp.","shortCitationAuthor":"Conant and Collins","shortCitationYear":1998,"referenceCode":"B98CON01EHUS","lastModified":"2020-02-25T18:11:57.819328Z"},{"id":621810,"citation":"Crother, B. I. (editor). 2008. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. Sixth edition. Society for the Study of Amphibians and Reptiles Herpetological Circular 37:1-84. Online with updates at: http://www.ssarherps.org/pages/comm_names/Index.php","shortCitationAuthor":"Crother","shortCitationYear":2008,"referenceCode":"B08CRO01NAUS","lastModified":"2020-02-25T14:38:20.142383Z"},{"id":722484,"citation":"Crother, B. I. (editor). 2012. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. 7th edition. 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Auburn University Agricultural Experiment Station, Auburn, Alabama. vii + 347 pp.","shortCitationAuthor":"Mount","shortCitationYear":1975,"referenceCode":"B75MOU01NAUS","lastModified":"2020-02-25T18:11:56.616394Z"},{"id":1153425,"citation":"Nicholson, K. E. (ed.). 2025. Scientific and Standard English Names of Amphibians and Reptiles of North America North of Mexico, with Comments Regarding Confidence in Our Understanding. Ninth Edition. Society for the Study of Amphibians and Reptiles. 87 pp. Online database available at: https://cnah.org/SSARnames.aspx","shortCitationAuthor":"Nicholson","shortCitationYear":2025,"referenceCode":"B25NIC01NAUS","lastModified":"2026-06-06T01:36:32.018241Z"},{"id":146382,"citation":"Phillips, C. A., R. A. Brandon, and E. O. Moll. 1999. Field guide to amphibians and reptiles of Illinois. 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University of Arkansas Press.","shortCitationAuthor":"Trauth et al.","shortCitationYear":2004,"referenceCode":"B04TRA01NAUS","lastModified":"2020-02-25T18:11:58.163079Z"}],"otherCommonNames":[{"id":145046,"name":"Mississippi green watersnake","language":"EN"},{"id":117778,"name":"Mississippi Green Water Snake","language":"EN"}],"speciesGlobal":{"elementGlobalId":105757,"cites":null,"cosewic":null,"fwsRegion":null,"genusSize":{"id":3,"genusSizeDescEn":"Small genus","genusSizeDescEs":"Género pequeño","genusSizeDescFr":"Petit genre"},"jurisEndem":{"id":3,"jurisEndemDescEn":"endemic to a single nation","jurisEndemDescEs":"Endémico de una nación","jurisEndemDescFr":"Endémique à une nation"},"nomenclaturallyEst":null,"usesa":null,"informalTaxonomy":{"informalTaxonomyId":7,"level1":"Animals","level2":"Vertebrates","level3":"Reptiles","level":3,"hasChildren":false,"parentId":2,"distributionStatus":"complete","displayOrder":1100},"parentSpecies":null,"infraspecies":false,"kingdom":"Animalia","phylum":"Craniata","taxclass":"Reptilia","taxorder":"Squamata","family":"Colubridae","genus":"Nerodia","americanFisheriesStatus":null,"americanFisheriesStatusDate":null,"saraStatus":null,"saraStatusDate":null,"cosewicDate":null,"interpretedCosewic":null,"cosewicComments":null,"usesaDate":null,"interpretedUsesa":null,"usesaComments":null,"completeDistribution":true,"synonyms":[{"id":101949,"synonym":"Natrix cyclopion","synonymAuthor":null,"formattedSynonym":"<i>Natrix cyclopion</i>"}],"infraspeciesList":[],"ebarId":null,"ebarCanadianScope":false,"ebarGlobalScope":false,"ebarKbaGroup":"Amphibians and Reptiles","caGeneralStatusId":null},"speciesCharacteristics":{"elementGlobalId":105757,"reproductionComments":"Gives birth to 4-101 young, June-September (Fitch 1970).","ecologyComments":null,"habitatComments":"Habitats include marshes, forested swamps, ditches, canals, bayous, shallow lakes and ponds, wet coastal prairie, oxbows and floodplain sloughs, sluggish tree-lined streams, flooded fields, abandoned rice fields, and rice field reservoirs, often quiet waters of wooded areas; also some brackish-water marshes along the Gulf Coast (Dundee and Rossman 1989, Werler and Dixon 2000, Ernst and Ernst 2003, Trauth et al. 2004). 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