• Proposed
  • Under Assessment
  • VUPreliminary Assessed
  • 4Assessed
  • 5Published

Piptoporus quercinus (Schrad.) P. Karst.

Go to another Suggested Species...

Scientific name
Piptoporus quercinus
(Schrad.) P. Karst.
Common names
oak polypore
IUCN Specialist Group
Mushroom, Bracket and Puffball
Assessment status
Preliminary Assessed
Preliminary Category
VU C2a (i)
Proposed by
Ibai Olariaga Ibarguren
Martyn Ainsworth, Ibai Olariaga Ibarguren
Andreas Gminder, Tsutomu Hattori, Ivona Kautmanova, Tommy Knutsson, Martin Livezey, Thomas Læssøe
Comments etc.
Anders Dahlberg, Beatrice Senn-Irlet, Tatyana Svetasheva

Assessment Status Notes

Taxonomic notes

This species has been often referred to as Piptoporus quercinus (Schrad.) P. Karst, but its correct placement should be in Buglossoporus, as it is not closely related to P. betulinus, type of Piptoporus, as shown by molecular data (Binder et al. 2013). Buglossoporus quercinus is a polypore recognized by its fleshy and soft basidiomata, yellow and white pileus becoming brownish with age. Its fruiting populations are characteristic of large oak trees and medieval oak landscapes. It produces a brown rot.

Why suggested for a Global Red List Assessment?

Buglossoporus quercinus (=B. pulvinus, Piptoporus quercinus) is a well-known and conspicuous annual polypore associated with old large oak trees, causing brown rot. The primary causes of its decline are the scarceness of veteran oak trees, habitat fragmentation and suppression or death of host trees caused by densification of habitats due to change of land-use. It is red-listed in at least 8 countries: Denmark (EN), Czech Republic (VU), Germany (VU), Lithuania, Norway (EN, C2a(i)), Slovakia (EN),  Spain, Sweden, (EN, C2a (i)), United Kingdom.

Preliminary global (and European) red-list assessment: C2a (i) (VU) due to less than 3500 mature individuals (i.e. max. 2500), much less than 500 localities on a global scale (350 estimated), and a habitat in marked decline in both area and habitat quality. No subpopulation consist of more than 500 mature individuals, real figure probably far less, normal situation is just a few infected host trees in each locality. Small subpopulations and more and more fragmented distribution make the species very susceptible for local extinctions due to generation-gap in suitable host trees.

Geographic range

The species is distributed in temperate decidious forests of Europe and West Asia (Palearctic region), strictly following the distribution of Quercus robur. It is rare throughout its distribution range. In Europe the countries with most reports are Sweden and the United Kingdom, probably due to the relatively high occurrences of large oak trees in these countries. The European (global?) stronghold for this species is definitely the former royal hunting forest in England (Windsor Crown Estate) where 100 oaks are known to be occupied by this fungus (since 1998). This is roughly half the total number recorded for the UK as a whole (since 1960).

Population and Trends

Buglossoporus quercinus is estimated to be present in ca. 350 localities in Europe (incl. estimated unrecorded localities). The number of individuals estimated to exist in Europe is c. 1800. Its potential distribution area is large, but the scarceness of ancient Quercus trees in semi-open situations is a limiting factor for its presence. As ancient oak woodlands have disappeared to large extent during the past 100 years, populations of B. quercinus have decreased similarily. A cautious estimate of this habitat loss is 30-50% in a 100y perspective. Furthermore, the survivial of B. quercinus in future is challenged by the scarcity and long time-scale of large ancient oak trees able to fill in the generation-gap of veteran trees.

Population Trend: Deteriorating

Habitat and Ecology

Buglossoporus quercinus is associated with large old oak trees (Quercus robur), producing brown rot. It primarily occurs in relatively open habitats such as wood pastures, parklands and other mosaic decidious forests. Fruiting both on living trees and on logs and snags on dead wood some years after the death of the tree. This species has been stated to fruit only on trees older than 250 years (Crockatt 2008), but it has been observed fruiting on younger trees with exposed heartwood (veterans not ancients) under special circumstances (i.e. in core populations with small oak pollards or oaks that have been damaged when young and surrounded by relatively large and thriving populations of the fungus).

Temperate Forest


The main threat to B. quercinus is the rapid decrease of suitable host trees (Quercus, usually Q. robur) by forestry or changes in land management. Most of the still existing large oak tree areas in Europe have historically been used as grazed woodlands (pasture woodland) resulting in a semi-open environment. Death of large oak trees is accelerated by the decrease of grazing in pastoral landscapes (dense growth of competing understory trees and shrubs), change of land use to agriculture (ploughing close to trees, damage and trampling due to animal stocking density), to conifer forestry or to use as golf courses. In some areas cessation of pollarding could result in hastened death of oak trees. Habitat fragmentation might well be an additional threat that is increasing. Small population size make the species very susceptible for random events and local extinctions due to generation-gap in suitable host trees.

Residential & commercial developmentShifting agricultureUnintentional effects: large scale (species being assessed is not the target) [harvest]

Conservation Actions

Site protection and habitat management is urgently needed for localities. management plans must include proper clearing around veteran oaks harbouring B. quercinus in order to prolong the lifespan of oak trees. In some cases, a periodical pollarding can ensure a longer life of oak trees but caution is advised when starting to restore management of lapsed pollards. Fallen dead branches (often removed esp. in parks)  should be left in situ or moved to less formally managed areas to allow the fungus to fruit. Focusing on demography of oak population is very important, i.e. favouring younger oaks of different age classes as B. quercinus requires a continuous supply of ancient and/or veteran host trees in order to fruit.

Site/area protectionSite/area management

Research needed

Find figures as to the habitat decline. Species proposed as redlisted earlier on the European level. Population genetic research across Europe is needed as a preliminary limited study (using somatic incompatibility testing in UK) suggested that many genets may be genetically rather similar to each other (historical bottleneck?). Test the hypothesis that each occupied oak is inhabited by a single genet which can then fragment to several ramets as occupied branches and trunks fall to the ground.

TaxonomyPopulation size, distribution & trendsHabitat trends

Use and Trade


Ainsworth, A.M. 2017. Non-lichenised fungi. In: Ancient oaks in the English landscape (A. Farjon), RBG Kew.

Binder, M.; Justo, A.; Riley, R.; Salamov, A.; Lopez-Giraldez, F.; Sjökvist, E.; Copeland, A.; Foster, B.; Sun, H.; Larsson, E.; Larsson, K.-H.; Townsend, J.; Grigoriev, I.V. & Hibbett, D.S. 2013. Phylogenetic and phylogenomic overview of the Polyporales. Mycologia 105(6):1350-73.

Calonge, F.D.; García, A.; Sanz, M.; Bastardo, J. 2003. Buglossoporus quercinus (Basidiomycotina, Coriolaceae), nueva cita para España. Bol. Soc. Micol. Madrid 27: 33-35.

Crockatt, M. 2008. Ecology of the rare oak polypore Piptoporus quercinus
and the tooth fungi Hericium cirrhatum. H. coralloides. and H. erinaceus in the UK. Ph. D. dissertation. Proquest. LLC. University of Cardiff.

Farjon, A. 2017. Ancient oaks in the English landscape.  RBG Kew.

Sunhede, S. & Vasiliauskas, R. 2003. Hotade tickor på ek i Litauen. [Threatened polypores on oak in Lithuania.] – Svensk Bot. Tidskr. 97: 252–265. Uppsala. 0039-646X.

Known distribution - countries

Regional Population and Trends

Country Trend Redlisted