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Invasive plants, such as Amur honeyscuckle (<i>L</i><i>onicera maackii</i>) and common reed (<i>Phragmites australis</i>), can introduce contaminants into water sources and make them unsuitable for this species (Dodd Jr. 2023).","shortTermTrendComments":"This species is generally considered to be declining (Dodd Jr. 2023).","longTermTrendComments":"This species has suffered local extirpations in some parts of the range and is generally considered to have declined in abundance, though it was never highly abundant (Dodd Jr. 2023).","inventoryNeeds":"Range-wide surveys needed. Surveys should take place over multiple years to accurately determine presence.","numberProtEosComments":"There are many occurrences on conservation lands.","protectionNeeds":null,"otherConsiderations":null,"intrinsicVulnerabilityComments":null,"enviromentalSpecificityComments":"This species occupies a variety of wetland habitats with a preference for cool water (Dodd Jr. 2023)."},"animalCharacteristics":{"elementGlobalId":101857,"majorHabitat":null,"nonMigrant":true,"localMigrant":false,"longDistanceMigrant":false,"mobilityMigrationComments":null,"foodHabitsComments":"Metamorphosed frogs eat various small invertebrates, terrestrial and aquatic. Larvae probably eat mostly suspended matter, algae, plant tissue, organic debris, and minute organisms in water.","animalPhenologyComments":"n the northern part of the range, pickerel frogs are mostly inactive during the coldest winter months.","colonialBreeder":false,"length":9,"width":null,"weight":null,"animalPhenologies":[{"animalCagPhenologyId":101590,"animalPhenology":{"id":1,"animalPhenologyDescEn":"Hibernates/aestivates","animalPhenologyDescEs":"Hibernación/Estivación","animalPhenologyDescFr":"Hiberne/estive","displayOrder":1},"adult":true,"immature":true},{"animalCagPhenologyId":101591,"animalPhenology":{"id":2,"animalPhenologyDescEn":"Circadian","animalPhenologyDescEs":"Circadiano","animalPhenologyDescFr":"Circadien","displayOrder":2},"adult":true,"immature":true}],"animalFoodHabits":[{"animalCagFoodHabitsId":103012,"foodHabits":{"id":3,"foodHabitsDescEn":"Invertivore","foodHabitsDescEs":"Invertívoro","foodHabitsDescFr":"Invertivore","displayOrder":3},"adult":true,"immature":false},{"animalCagFoodHabitsId":103013,"foodHabits":{"id":4,"foodHabitsDescEn":"Herbivore","foodHabitsDescEs":"Herbívoro","foodHabitsDescFr":"Herbivore","displayOrder":4},"adult":false,"immature":true}]},"occurrenceDelineations":[{"eoSpecsDetailId":1179,"locationUseClass":{"id":1,"locationUseClassDescEn":"Not applicable","locationUseClassDescEs":"No se aplica","locationUseClassDescFr":"Sans objet","displayOrder":1},"eoSpecGroupName":"Ranid Frogs","subtypes":"Breeding Location","inferredExtentDistance":null,"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 larvae or eggs) in or near appropriate habitat where the species is presumed to be established and breeding.","mappingGuidance":null,"separationBarriers":"Busy major highway, especially at night, such that frogs rarely if ever cross successfully; urban development dominated by buildings and pavement; habitat in which site-specific data indicate the frogs virtually never occur.","separationDistanceUnsuitableHabitatat":1.0,"separationDistanceSuitableHabitatat":5.0,"altSeparationProcedure":null,"separationJustification":"BARRIERS/UNSUITABLE HABITAT: Rivers may or may not be effective barriers, depending on stream width and flow dynamics; identification of streams as barriers is a subjective determination. Ranid frog species vary in habitat use, but even the most aquatic species may traverse upland habitat when conditions are suitable (Pope and Matthews 2001); natural and seminatural upland habitat generally does not constitute a barrier. Here, unsuitable habitat refers to upland habitat devoid or nearly devoid of wetlands, streams, ponds, or lakes. Bodies of water dominated by predatory fishes may be barriers to some species but suitable habitat for others; in most cases, such waters probably should be regarded as unsuitable habitat.<br /><br />SUITABLE HABITAT (Applies to most North American ranids, but not <i>Lithobates sevosa</i> or <i>L. </i><i>capit</i>o): Suitable habitat includes riparian/riverine corridors, wetlands, and wetland/upland mosaics in which wetland patches are separated by less than 1 km of upland habitat; it also includes any upland habitat regularly used for feeding or wintering (e.g., mesic forest for wood frogs).<br /><br />MOVEMENTS (Applies to most North American ranids, but not <i>Lithobates sevosa</i> or <i>L. </i><i>capit</i>o): Available information indicates that individual ranids occasionally move distances of several km (<i>R. luteiventris</i>: Reaser 1996, cited by Koch et al. 1997; <i>R. blairi</i>: Gillis 1975) but most individuals stay within a few kilometers of their breeding sites (<i>R. aurora draytonii</i>: USFWS, Federal Register, 11 September 2000; <i>L. capito</i>: Franz et al. 1988; <i>R. clamitans</i>: Lamoureux and Madison 1999; <i>R. luteiventris</i>: Turner 1960, Hollenbeck 1974, Bull and Hayes 2001). Similarly, maximum distance between capture points generally is a few kilometers or less (<i>R. aurora</i>: Hayes et al. 2001; USFWS, Federal Register, 11 September 2000; <i>L. catesbeiana</i>: Willis et al. 1956; <i>R. luteiventris</i>: Reaser and Pilliod, in press; Engle 2000; <i>R. muscosa</i>: Pope and Matthews 2001). Dispersal data for juveniles are lacking for most species.<br /><br />Adult and juvenile <i>L. sylvaticus</i> readily traveled in excess of 300 m from their pools of origin (Vasconcelos and Calhoun 2004). Bellis (1965) determined that adult and juvenile <i>L. sylvaticus</i> in a peat bog had traveled at least 410 m from the nearest breeding pool. Berven and Grudzien (1990) found that dispersing <i>L. sylvaticus</i> juveniles traveled an average of 1,208 m from their natal pools. In the Shenandoah Mountains, data for <i>L. sylvaticus</i> indicated that ponds separated by a distance greater than 1,000 m should experience little gene flow (Berven and Grudzien 1991). In contrast, populations in Minnesota were very similar in allelic frequencies, even at distances greater than several kilometers (Squire and Newman 2002). However, sample sizes and number of loci examined were small, and genetic patterns do not necessarily reflect movement distances.<br /><br />See Humphries and Sisson (2012) for information about movements, habitat needs, and area requirements for <i>L. capito</i>.<br /><br />The preponderance of data for ranids indicate that a separation distance of several kilometers may be appropriate for suitable habitat and practical for occurrence delineation, despite occasional movements that are longer and that may allow some genetic interchange between distant populations. The movement data for ranids are here regarded as consistent enough to allow the same separation distance to be used for different species; much of the apparent variation in movements doubtless reflects differences in study methods and in the ability to detect long-distance movements.","versionDate":"2005-04-01","versionAuthor":"Hammerson, G.","versionNotes":null,"lastModified":"2020-10-03T20:47:46.301189Z"}],"plantCharacteristics":null,"elementManagement":{"elementGlobalId":101857,"eoManagementGroupName":null,"stewardshipOverview":null,"impacts":null,"restorationPotential":null,"siteConservationPlansConsidered":null,"managementMethods":null,"monitoringMethods":null,"managementProgramContacts":null,"monitoringProgramContacts":null,"managementResearchPrograms":null,"managementResearchNeeds":null,"biologicalResearchNeeds":"Research is needed on <i>in situ</i> impacts of chytrid.","additionalTopics":null},"occurrenceViabilities":[{"eoRankSpecsDetailId":103387,"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":"2020-05-14T02:20:03.097741Z"}],"references":[{"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":112779,"citation":"Blackburn, L., P. Nanjappa, and M. J. Lannoo. 2001. An Atlas of the Distribution of U.S. Amphibians. Copyright, Ball State University, Muncie, Indiana, USA.","shortCitationAuthor":"Blackburn et al.","shortCitationYear":2001,"referenceCode":"B01BLA01EHUS","lastModified":"2020-02-25T14:38:24.173666Z"},{"id":1167418,"citation":"Che, J., J. Pang, E. M. Zhao, M. Matsui, and Y. P. Zhang. 2007. Phylogenetic relationships of the Chinese brown frogs (genus <i>Rana</i>) inferred from partial mitochondrial 12S and 16S rRNA gene sequences. Zoological Science 24(1):71-80.","shortCitationAuthor":"Che et al.","shortCitationYear":2007,"referenceCode":"A07CHE02NAUS","lastModified":"2026-06-06T01:37:34.510214Z"},{"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":943912,"citation":"Crother, B. I. (editor). 2017. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. 8th edition. SSAR Herpetological Circular 43:1-104. [Updates in SSAR North American Species Names Database at: https://ssarherps.org/cndb]","shortCitationAuthor":"Crother","shortCitationYear":2017,"referenceCode":"B17CRO01EHUS","lastModified":"2020-02-25T18:11:53.413199Z"},{"id":115940,"citation":"DeGraaf, R. M., and D. D. Rudis. 1983a. Amphibians and reptiles of New England. Habitats and natural history. Univ. Massachusetts Press. vii + 83 pp.","shortCitationAuthor":"DeGraaf and Rudis","shortCitationYear":1983,"referenceCode":"B83DEG01NAUS","lastModified":"2020-02-25T18:12:26.951601Z"},{"id":1154950,"citation":"Dodd, C. K., Jr. 2023. Frogs of the United States and Canada, Second Edition. Johns Hopkins University Press, Baltimore, MD.","shortCitationAuthor":"Dodd Jr.","shortCitationYear":2023,"referenceCode":"B23DOD01NAUS","lastModified":"2025-07-03T21:50:15.223155Z"},{"id":1107242,"citation":"Dubois, A., A. Ohler, and R. A. Pyron. 2021. New concepts and methods for phylogenetic taxonomy and nomenclature in zoology, exemplified by a new ranked cladonomy of recent amphibians (Lissamphibia). Megataxa 5:1-738.","shortCitationAuthor":"Dubois et al.","shortCitationYear":2021,"referenceCode":"A21DUB01NAUS","lastModified":"2021-12-06T19:01:16.251202Z"},{"id":997759,"citation":"Elliott, W. R. 2003. A guide to Missouri's cave life: 70 species brought to life. Missouri Department of Conservation. 37 pp.","shortCitationAuthor":"Elliott","shortCitationYear":2003,"referenceCode":"B03ELI01EHUS","lastModified":"2020-02-25T18:12:52.476544Z"},{"id":119796,"citation":"Frost, D. R. 1985. Amphibian species of the world. A taxonomic and geographical reference. Allen Press, Inc., and The Association of  Systematics Collections, Lawrence, Kansas. v + 732 pp.","shortCitationAuthor":"Frost","shortCitationYear":1985,"referenceCode":"B85FRO01HQUS","lastModified":"2020-02-25T14:38:24.173666Z"},{"id":650580,"citation":"Frost, D. R. 2010. Amphibian Species of the World: an Online Reference. Version 5.4 (8 April 2010). Electronic Database accessible at http://research.amnh.org/herpetology/amphibia/index.php. American Museum of Natural History, New York, USA. ","shortCitationAuthor":"Frost","shortCitationYear":2010,"referenceCode":"W10FRO01NAUS","lastModified":"2020-02-25T14:38:15.579798Z"},{"id":1054360,"citation":"Frost, D.R. 2020. Amphibian Species of the World: an Online Reference. Version 6.0. American Museum of Natural History, New York, USA. Online: http://research.amnh.org/herpetology/amphibia/index.html","shortCitationAuthor":"Frost","shortCitationYear":2020,"referenceCode":"W20FRO02NAUS","lastModified":"2020-02-25T19:41:47.447453Z"},{"id":614712,"citation":"Frost, D.R., T. Grant, J. Faivovich, R. Bain, A. Haas, C.F.B. Haddad, R.O. de Sa´, S.C. Donnellan, C.J. Raxworthy, M. Wilkinson, A. Channing, J.A. Campbell, B.L. Blotto, P. Moler, R.C. Drewes, R.A. Nussbaum, J.D. Lynch, D. Green, and W.C. Wheeler. 2006. The amphibian tree of life. Bulletin of the American Museum of Natural History 297: 1-370.","shortCitationAuthor":"Frost et al.","shortCitationYear":2006,"referenceCode":"B06FRO01NAUS","lastModified":"2020-02-25T18:12:01.663271Z"},{"id":113717,"citation":"Holomuzki, J. R. 1995. Oviposition sites and fish-deterrent mechanisms of two stream anurans. 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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":715786,"citation":"Newman, C.E., J.A. Feinberg, L.J. Rissler, J. Burger, and H.B. Shaffer. 2012. A new species of leopard frog (Anura: Ranidae) from the urban northeastern US. Molecular Phylogenetics and Evolution 63(2):445-455.","shortCitationAuthor":"Newman et al.","shortCitationYear":2012,"referenceCode":"A12NEW01NAUS","lastModified":"2020-02-25T19:55:31.037972Z"},{"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":130762,"citation":"Pace, A.E. 1974. Systematic and biological studies of the leopard frogs (<i>Rana pipiens</i> Complex) of the United States. Misc. Publ. Mus. Zool., Univ. Michigan 148:1-140.","shortCitationAuthor":"Pace","shortCitationYear":1974,"referenceCode":"A74PAC01NAUS","lastModified":"2021-07-03T03:58:51.386341Z"},{"id":124569,"citation":"Schaaf, R. T., Jr., and P. W. Smith. 1971. <i>Rana palustris</i>. Cat. Am. Amph. Rep. 117.1-117.3.","shortCitationAuthor":"Schaaf and Smith","shortCitationYear":1971,"referenceCode":"A71SCH01NAUS","lastModified":"2021-07-03T03:58:51.386341Z"},{"id":132352,"citation":"Vogt, R. C. 1981c. Natural history of amphibians and reptiles of Wisconsin. Milwaukee Public Museum. 205 pp.","shortCitationAuthor":"Vogt","shortCitationYear":1981,"referenceCode":"B81VOG01NAUS","lastModified":"2020-02-25T18:12:18.569643Z"},{"id":1064767,"citation":"Yuan, Z.-Y, W.-W. Zhou, X. Chen, N.A. Poyarkov Jr, H.-M. Chen, N.-H. Jang-Liaw, W.-H. Chou, N.J. Matzke, K. Iizuka, M.-S. Min, S.L. Kuzmin, Y.-P. Zhang, D.C. Cannatella, D.M. Hillis, and J. Chesp. 2016. Spatiotemporal diversification of the true frogs (genus <i>Rana</i>): a historical framework for a widely studied group of model organisms. Systematic biology 65(5):824-842.","shortCitationAuthor":"Yuan et al.","shortCitationYear":2016,"referenceCode":"A16YUA01NAUS","lastModified":"2020-10-03T21:02:13.064178Z"}],"otherCommonNames":[{"id":134821,"name":"Grenouille des marais","language":"FR"},{"id":144896,"name":"pickerel frog","language":"EN"}],"speciesGlobal":{"elementGlobalId":101857,"cites":null,"cosewic":{"id":6,"cosewicDescEn":"Not at Risk","cosewicDescEs":"No está en riesgo","cosewicDescFr":"Non en péril","cosewicCode":"NAR"},"fwsRegion":null,"genusSize":{"id":4,"genusSizeDescEn":"Medium to large genus","genusSizeDescEs":"Género de mediano a grande","genusSizeDescFr":"Moyen à grand genre"},"jurisEndem":{"id":5,"jurisEndemDescEn":"occurs (regularly, as a native taxon) in multiple nations","jurisEndemDescEs":"Se encuentra en varias naciones (de manera regular, como un taxón nativo)","jurisEndemDescFr":"Se trouve dans plusieurs nations (de façon régulière, tel un taxon indigène)"},"nomenclaturallyEst":null,"usesa":null,"informalTaxonomy":{"informalTaxonomyId":3,"level1":"Animals","level2":"Vertebrates","level3":"Amphibians","level":3,"hasChildren":false,"parentId":2,"distributionStatus":"complete","displayOrder":1060},"parentSpecies":null,"infraspecies":false,"kingdom":"Animalia","phylum":"Craniata","taxclass":"Amphibia","taxorder":"Anura","family":"Ranidae","genus":"Lithobates","americanFisheriesStatus":null,"americanFisheriesStatusDate":null,"saraStatus":null,"saraStatusDate":null,"cosewicDate":"1999-04-01","interpretedCosewic":null,"cosewicComments":"Reason for Designation: Populations of this frog species are scattered and fragmented. This species is suspected of being in decline in some parts of its range as a result of wetland drainage and forest conversion. Nevertheless, it remains widespread and it is evidently still abundant in the eastern part of its range.<br/><br/>Status History: Designated Not at Risk in April 1999. More recently (2015) considered a medium priority candidate for re-assessment.","usesaDate":null,"interpretedUsesa":null,"usesaComments":null,"completeDistribution":true,"synonyms":[{"id":115331,"synonym":"Rana palustris","synonymAuthor":"LeConte, 1825","formattedSynonym":"<i>Rana palustris</i>"}],"infraspeciesList":[],"ebarId":"168076","ebarCanadianScope":false,"ebarGlobalScope":false,"ebarKbaGroup":"Amphibians and Reptiles","caGeneralStatusId":"GS000745"},"speciesCharacteristics":{"elementGlobalId":101857,"reproductionComments":"Breeding occurs in winter in the far south, in spring (mostly April-May) in the north. Larvae hatch in several days or up to three weeks after laying, metamorphose usually within 2-3 months, in summer (often July-August in the north).","ecologyComments":"Pickerel frogs have a distinctive odor and bright colors that are thought to advertise their distasteful skin secretions, and some predators such as shrews, certain fishes, and common garter snakes may reject them as food. Larvae are palatable to some fishes (green sunfish), less palatable to others (longear sunfish) (Holomuzki 1995).","habitatComments":"Pickerel frogs occur in various freshwater aquatic and wetland habitats in wooded regions, ranging from the vicinity of cool clear streams and ponds in the north to warm, turbid swamps in parts of the south. In summer, they commonly range into fields and woods away from ponds or streams. In winter, they may be hidden at the bottom of a water body or secluded in wet caves.Breeding sites include standing water of woodland ponds, bog ponds, impoundments, stream pools, sloughs, and flooded ditches, often but not always in sites with few or no fishes (e.g., Holomuzki 1995). Males call while floating or submerged. Females attach egg masses to submerged vegetation.","generalDescription":"Upper surface is tan with two parallel rows of more or less rectangular dark spots along the middle of the back. The base of the hind legs and groin are yellow or orange, though this color is faint or absent in juveniles. A light stripe runs along the upper jaw. A glandualr ridge extends along each side of the back. The hind toes are extensively webbed. Maximum size is around 3.5 inches (8.7 cm) snout-vent length. Breeding males have forelimbs that are more massive than those of females and juveniles, and the base of the thumb is large in breeding males than in adult females. Breeding call is a low snore lasting 1-2 seconds. Larvae are not particularly distinctive; the upper side is green with small black and yellow spots; tail fins are low, with heavy dark mottling, and the eyes are not at the margins of the head when viewed from above. Maximum total length of larvae is about 3 inches (7.5 cm). Eggs are laid in firm spherical masses containing up to a few thousand eggs.","diagnosticCharacteristics":null,"speciesMarineHabitats":[],"speciesTerrestrialHabitats":[{"cagTerrHabId":-107140,"terrestrialHabitat":{"id":4,"terrestrialHabitatDescEn":"Woodland - Hardwood","terrestrialHabitatDescEs":"Lote de madera - Madera dura","terrestrialHabitatDescFr":"Terrain boisé — Feuillu","displayOrder":6}},{"cagTerrHabId":-107138,"terrestrialHabitat":{"id":8,"terrestrialHabitatDescEn":"Savanna","terrestrialHabitatDescEs":"Sabana","terrestrialHabitatDescFr":"Savane","displayOrder":10}},{"cagTerrHabId":-107139,"terrestrialHabitat":{"id":9,"terrestrialHabitatDescEn":"Grassland/herbaceous","terrestrialHabitatDescEs":"Pastizales/cobertura herbácea","terrestrialHabitatDescFr":"Prairie/couverture herbacée","displayOrder":11}}],"speciesRiverineHabitats":[{"cagRiverineHabId":-103563,"riverineHabitat":{"id":2,"riverineHabitatDescEn":"MEDIUM RIVER","riverineHabitatDescEs":"RÍO MEDIANO","riverineHabitatDescFr":"MOYENNE RIVIÈRE","displayOrder":2}},{"cagRiverineHabId":-103564,"riverineHabitat":{"id":3,"riverineHabitatDescEn":"CREEK","riverineHabitatDescEs":"ARROYO","riverineHabitatDescFr":"RUISSEAU","displayOrder":3}},{"cagRiverineHabId":-103566,"riverineHabitat":{"id":6,"riverineHabitatDescEn":"Moderate gradient","riverineHabitatDescEs":"Pendiente de flujo medio","riverineHabitatDescFr":"Pente d’écoulement moyenne","displayOrder":6}},{"cagRiverineHabId":-103567,"riverineHabitat":{"id":7,"riverineHabitatDescEn":"Low gradient","riverineHabitatDescEs":"Pendiente de bajo flujo","riverineHabitatDescFr":"Pente d’écoulement faible","displayOrder":7}},{"cagRiverineHabId":-103565,"riverineHabitat":{"id":9,"riverineHabitatDescEn":"Pool","riverineHabitatDescEs":"Piscina","riverineHabitatDescFr":"Fosse","displayOrder":9}}],"speciesPalustrineHabitats":[{"cagPalusHabId":-101847,"palustrineHabitat":{"id":1,"palustrineHabitatDescEn":"TEMPORARY POOL","palustrineHabitatDescEs":"PISCINA TEMPORAL","palustrineHabitatDescFr":"BASSIN TEMPORAIRE","displayOrder":1}},{"cagPalusHabId":-101848,"palustrineHabitat":{"id":2,"palustrineHabitatDescEn":"HERBACEOUS WETLAND","palustrineHabitatDescEs":"HUMEDAL HERBÁCEO","palustrineHabitatDescFr":"TERRE HUMIDE HERBACÉE","displayOrder":2}},{"cagPalusHabId":-101849,"palustrineHabitat":{"id":3,"palustrineHabitatDescEn":"SCRUB-SHRUB WETLAND","palustrineHabitatDescEs":"HUMEDAL DE MATORRALES","palustrineHabitatDescFr":"FRUTICÉE HUMIDE","displayOrder":3}},{"cagPalusHabId":-101850,"palustrineHabitat":{"id":4,"palustrineHabitatDescEn":"FORESTED WETLAND","palustrineHabitatDescEs":"HUMEDAL BOSCOSO","palustrineHabitatDescFr":"TERRE HUMIDE FORESTIÈRE","displayOrder":4}},{"cagPalusHabId":-101851,"palustrineHabitat":{"id":5,"palustrineHabitatDescEn":"Bog/fen","palustrineHabitatDescEs":"Pantanoso","palustrineHabitatDescFr":"Tourbière oligotrophe/marais","displayOrder":5}},{"cagPalusHabId":-101852,"palustrineHabitat":{"id":6,"palustrineHabitatDescEn":"Riparian","palustrineHabitatDescEs":"Ribereño","palustrineHabitatDescFr":"Riverain","displayOrder":6}}],"speciesLacustrineHabitats":[{"cagLacusHabId":-100527,"lacustrineHabitat":{"id":2,"lacustrineHabitatDescEn":"Shallow water","lacustrineHabitatDescEs":"Aguas poco profundas","lacustrineHabitatDescFr":"Eau peu profonde","displayOrder":2}}],"speciesSubterraneanHabitats":[],"speciesEstuarineHabitats":[]},"primaryReference":{"id":1153425,"citation":"Nicholson, K. 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