Peltigera gowardii

Lendemer & H. O'Brien

Western Waterfan Lichen

G3Vulnerable (G3G4) Found in 4 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
High - mediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.873613
Element CodeNLVER00460
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryFungus
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomFungi
PhylumAscomycota
ClassLecanoromycetes
OrderPeltigerales
FamilyPeltigeraceae
GenusPeltigera
Synonyms
Peltigera hydrothyria var. gowardii(Lendemer & O'Brien) McCune
Other Common Names
Peltigère éventail d'eau de l'Ouest (FR)
Concept Reference
Lendemer, J.C., and H. O'Brien. 2011. How do you reconcile molecular and non-molecular datasets? A case study where new molecular data prompts a revision of Peltigera hydrothyria s.l. in North America and the recognition of two species. Opuscula Philolichenum, 9: 99-110.
Taxonomic Comments
Lendemer & OBrien (2011) split Peltigera hydrothyria (Hydrothyria venosa). The name Peltigera hydrothyria was kept for eastern populations while western populations became Peltigera gowardii.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-03-26
Change Date2013-09-04
Edition Date2025-03-26
Edition AuthorsN. Ventrella (2025)
Threat ImpactHigh - medium
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Number of Occurrences21 - 80
Rank Reasons
Peltigera gowardii is an aquatic foliose lichen occurring in cool, clear, free-flowing streams with low nitrogen and neutral pH in western North America, where it is widely distributed in mountain regions from Alaska and British Columbia through Washington and Montana south to Wyoming and California in the United States and Canada. There are an estimated 80 occurrences of this species, with the bulk of its distribution located in the Oregon Cascades region south through California. Climate change is the primary threat to this species, which requires a narrow band of climactic conditions, and does not tolerate increases to water temperature. Additional threats include grazing, timber harvest, fuels reduction, herbicide, flooding, recreation, garbage dumping, trail and road development, dam construction, water diversion, and succession. There are taxonomic issues in this group which have made it difficult to identify western lichens to species, which has stymied conservation efforts. Further research is also needed to clarify trends for Peltigera gowardii.
Range Extent Comments
Peltigera gowardii occurs in western North America, where it is widely distributed in mountain regions from Alaska and British Columbia through Washington and Montana south to Wyoming and California in the United States and Canada (Lendemer and O'Brien 2011). A molecular study (Miadlikowska et al. 2014) found support for a split of P. gowardii into two species; P. gowardii, which extends from Washington state northward, and P. aquatica, which extends southward. However, the two species overlap in range, and are morphologically and chemically identical, making it impossible to identify this taxon to the species level without molecular analysis (McCune and Stone 2022). McCune and Stone (2022) proposed classifying all North American members of this group once again as P. hydrothyria with three varieties (vars. hydrothyria, gowardii, and aquatica). Due to the shifting taxonomy of the Peltigera hydrothyria complex, range extent and other rating factors included the following synonyms, following Dean (2023): Hydrothyria venosa, Peltigera gowardii, P. hydrothyria (of western distribution), and P. aquatica. Range extent was estimated using herbarium specimens, California Natural Diversity Database data, and NatureServe Network occurrence data collected between 1994 and 2025 (RARECAT 2024, CLH 2025, CNDDB 2025, GBIF 2025, NatureServe 2025).
Occurrences Comments
By applying a 1 km separation distance to herbarium specimens, California Natural Diversity Database data, and NatureServe Network occurrence data collected between 1994 and 2025, it is estimated that there are 80 element occurrences (RARECAT 2024, CLH 2025, CNDDB 2025, GBIF 2025, NatureServe 2025).
Threat Impact Comments
Peltigera gowardii is dependent on cool, clear, mountain streams in old growth forests and is primarily threatened by any actions altering water quality, quantity, temperature, sediment load, chemistry, light regime, or stream bank stability (Poulsen and Carlberg 2007). Climate change is a major threat to this species, which has a very narrow climactic tolerance and is highly correlated with low minimum winter temperatures (Glavich 2009). Temperature increases of upwards of 2.5 °C are predicted for the Pacific Northwest region during this century (Mote et al. 2003), which could make some of the current occupied habitat of this lichen uninhabitable (Glavich 2009). In addition, climate change could increase the frequency and severity of storms and flooding, which may scour Peltigera gowardii from stream channels during high flows. Additional threats to this species include timber harvest, fuels reduction efforts, herbicide use, livestock-related impacts (such as sedimentation, erosion, disturbance, and pollution from cattle), natural erosion and flooding, camping, and other recreational activities, disturbance and sedimentation caused by off-highway vehicles, garbage dumping, trail and road development, dam construction, water diversion, and succession of trees into mountain meadow habitats (COSEWIC 2013, Dean 2023, CNDDB 2025, CNPS 2025).
Ecology & Habitat

Habitat

Peltigera gowardii occurs at or below water levels in spring-fed streams with flowing, silt-free, cool water, usually of neutral pH (COSEWIC 2013). This lichen is generally found in streams in open subapline and alpine meadows and lower and upper montane conifer and riparian forests (COSEWIC 2013, Dean 2023). It is associated with older forests, and most frequently found on large rocks or bedrock at or just slightly above the water level (Glavich 2009).

Reproduction

Peltigera gowardii spores are presumably dispersed by air or water (COSEWIC 2013).
Other Nations (2)
United StatesN3
ProvinceRankNative
WyomingSNRYes
CaliforniaS3Yes
AlaskaS1Yes
OregonSNRYes
WashingtonS3Yes
MontanaS1Yes
IdahoSNRYes
CanadaN2
ProvinceRankNative
British ColumbiaS2Yes
Threat Assessments
ThreatScopeSeverityTiming
2 - Agriculture & aquacultureUnknownUnknownUnknown
2.3 - Livestock farming & ranchingUnknownUnknownUnknown
2.3.4 - Scale unknown/unrecordedUnknownUnknownUnknown
4 - Transportation & service corridorsUnknownUnknownUnknown
4.1 - Roads & railroadsUnknownUnknownUnknown
5 - Biological resource useUnknownUnknownUnknown
5.3 - Logging & wood harvestingUnknownUnknownUnknown
5.3.4 - Unintentional effects: large scale (species being assessed is not the target) [harvest]UnknownUnknownUnknown
6 - Human intrusions & disturbanceUnknownUnknownUnknown
6.1 - Recreational activitiesUnknownUnknownUnknown
7 - Natural system modificationsUnknownUnknownUnknown
7.1 - Fire & fire suppressionUnknownUnknownUnknown
7.1.2 - Suppression in fire frequency/intensityUnknownUnknownUnknown
7.2 - Dams & water management/useUnknownUnknownUnknown
9 - PollutionUnknownUnknownUnknown
9.3 - Agricultural & forestry effluentsUnknownUnknownUnknown
9.3.1 - Nutrient loadsUnknownUnknownUnknown
9.3.2 - Soil erosion, sedimentationUnknownUnknownUnknown
9.3.3 - Herbicides and pesticidesUnknownUnknownUnknown
9.4 - Garbage & solid wasteUnknownUnknownUnknown
11 - Climate change & severe weatherPervasive (71-100%)Serious - moderateHigh (continuing)
11.2 - DroughtsLarge (31-70%)Serious - moderateHigh (continuing)
11.3 - Temperature extremesPervasive (71-100%)Serious - moderateHigh (continuing)
11.4 - Storms & floodingLarge (31-70%)Serious - moderateHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (4)
California (1)
AreaForestAcres
CrapoKlamath National Forest1,487
Oregon (3)
AreaForestAcres
Bull Of The WoodsMt. Hood National Forest8,843
Echo MountainWillamette National Forest8,098
Opal CreekWillamette National Forest5,417
References (16)
  1. California Native Plant Society (CNPS), Rare Plant Program. 2025. Inventory of Rare and Endangered Plants of California, online edition, v9.5. Online. Available: https://www.rareplants.cnps.org (accessed 2025).
  2. California Natural Diversity Database (CNDDB). 2025. RareFind Version 5.3.0. California Department of Fish and Game, Sacramento.
  3. Committee on the Status of Endangered Wildlife in Canada (COSEWIC). 2013. COSEWIC assessment and status report on the Western Waterfan <i>Peltigera gowardii</i> in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xi + 39 pp. Online. Available: www.registrelep-sararegistry.gc.ca/default_e.cfm (accessed 2025).
  4. Consortium of Lichen Herbaria. 2025. https://lichenportal.org/portal/index.php (accessed 2025).
  5. Dean, Ellen A. 2023. Status Review: <i>Peltigera gowardii</i> Lendemer & H. O'Brien, western waterfan lichen. California Native Plant Society and California Natural Diversity Database. 31 October 2023.
  6. Esslinger, T. L. 2018. A cumulative checklist for the lichen-forming, lichenicolous and allied fungi of the continental United States and Canada, Version 22. Opuscula Philolichenum 17:6-268. [http://sweetgum.nybg.org/philolichenum/]
  7. Glavich, D.A. 2009. Distribution, rarity and habitats of three aquatic lichens on federal land in the US Pacific Northwest. The Bryologist 112(1): 54-72.
  8. Global Biodiversity Information Facility (GBIF). 2025. Global Biodiversity Information Facility (GBIF) data portal. Online. Available: https://www.gbif.org/ (accessed 2025).
  9. Hutten, M., U. Arup, O. Breuss, T. L. Esslinger, A. M. Fryday, K. Knudsen, J. C. Lendemer, C. Printzen, H. T. Root, M. Schultz, J. Sheard, T. Tønsberg, and B. McCune. 2013. Lichens and Lichenicolous Fungi of Yosemite National Park, California. North American Fungi 8(11): 1-47. doi: http://dx.doi:10.2509/naf2013.008.011
  10. Lendemer, J.C., and H. O'Brien. 2011. How do you reconcile molecular and non-molecular datasets? A case study where new molecular data prompts a revision of <i>Peltigera hydrothyria </i>s.l. in North America and the recognition of two species. Opuscula Philolichenum, 9: 99-110.
  11. McCune, B. and D.F. Stone. 2022. Eight new combinations of North American macrolichens. Evansia 39(3): 123-128.
  12. Miadlikowska, J., Richardson, D., Magain, N., Ball, B., Anderson, F., Cameron, R., Lendemer, J., Truong, C. and F. Lutzoni. 2014. Phylogenetic placement, species delimitation, and cyanobiont identity of endangered aquatic <i>Peltigera</i> species (lichen-forming Ascomycota, Lecanoromycetes). American Journal of Botany 101(7): 1141-1156.
  13. Mote, P.W., Parson, E.A., Hamlet, A.F., Keeton, W.S., Lettenmaier, D., Mantua, N., Miles, E.L., Peterson, D.W., Peterson, D.L., Slaughter, R. and A. K. Snover. 2003. Preparing for climatic change: the water, salmon, and forests of the Pacific Northwest. Climatic change 61: 45-88.
  14. NatureServe. 2025. NatureServe Network Biodiversity Location Data. NatureServe, Arlington, Virginia.
  15. NatureServe's Rapid Analysis of Rarity and Endangerment Conservation Assessment Tool (RARECAT). 2024. Version: 1.1.1 (released Oct 01, 2024).
  16. Poulsen, B. and T. Carlberg, T. 2007. <i>Peltigera hydrothyria</i>, sponsorship for the CALS Conservation Committee. Bulletin of the Californian Lichen Society 14: 15-18.