THE NATIONAL RED LIST OF NORTH MACEDONIA

Dupain’s bolete

Rubroboletus dupainii

Macedonian

Сјајно-црвен вргањ

Albanian

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Taxonomy
Assessment info
Population
Habitat and Ecology
Threats
Use and Trade
Conservation Actions
Bibliography

Taxonomy

Scientific name

Rubroboletus dupainii

Authority

(Boudier) Kuan Zhao & Zhu L. Yang

Synonyms

Boletus dupainii Boud.

Suillellus dupainii (Boud.) Blanco-Dios

Assessment info

IUCN Red List Category and Criteria

VU – Vulnerable D1

Date assessed

November 2020

Assessors

Tofilovska, S.

Reviewers

Kost, G.

Mešić, A.

Contributors

Karadelev, M.

Rusevska, K.

Facilitators

Miskovic, M.

Justification

Rubroboletus dupainii is a mycorrhizal species primarily with Quercus, and rarely with Fagus and Castanea. It inhabits old-growth thermophilous forests, on calcareous shallow soils. It has been sighted at only a single location, in Jablanica Mountain, at an elevation varying between 700 and 850 m. A population size between 200 and 400 mature individuals is estimated. Due to anthropogenic pressure, the favourable habitat type is heavily degraded. Besides forest exploitation, the habitat is affected by excavation of raw minerals. However, additional data is needed in order to estimate precisely the population trend of the fungus. Therefore, the species is categorized as vulnerable under criteria D1.

Population

Current population trend

Unknown.

Description

At the sole observed site, only one mature individual has been ascertained. Since natural, old-growth oak forests providing favourable conditions for R. dupainnii are scarce, a population size between 200 and 400 mature individuals is estimated. The estimation is based on: the probable total number of sites in the country (ca. 10, up to 20), the estimated number of functional individuals at each site (estimated to be two) and the template of how many mature individuals each reproducing genotype may give rise to (the template used ten) according to the instructions provided by Dahlberg and Mueller (2011). Exploitation of forests, forming of bare land, and diminished habitat quality is observed, however additional data is needed in order to estimate precisely the population trend of the fungus.

Habitat and Ecology

System

Terrestrial.

Habitat and Ecology

It is a mycorrhizal species mainly with Quercus, and rarely with Fagus and Castanea. It inhabits old-growth thermophilous forests, on calcareous shallow soils, sometimes preferring more open areas (Fraiture and Otto 2015). The species produces sporocarps in summer and autumn. According to Perini & Gonçalves (2019), at a global level the habitats where this species thrives are favorable in range and area but unfavorable in both structure & function. The expectations are that the species will move northwards in Europe, occupying potentially suitable habitats as a result of climate change effects.

In North Macedonia it has been documented at only a single site in the country, in Jablanica Mt, growing in oak forest on calcareous soil, at an elevation ranging between 700 and 850 m. Despite the fact that it is a conspicuous fungus and easy to be identified, it has not been recorded often, since a well-preserved, fitting thermophilous oak forests is scarcely found in the country. Therefore, the probable total number of sites is ca. 10, up to 20. The unremitting, strong anthropogenic influence upon the appropriate habitat is the reason for being so rare given that the species is regarded as sensitive to degradation of natural forests (Fraiture and Otto 2015).

Use and trade

Use and trade

It is not edible. It is suspected to be slightly poisonous. It is not subject of trade.

Threats

Threats

Oaks are the dominant forest in the country, occupying 29.3% of the total area but they also comprise the most degraded stands, especially the distinctly thermophilous forests (Kolevska et al. 2017). The species is generally threatened by continuous loss and fragmentation of oak forests due to logging activities. Forest exploitation has been practised for centuries, and at the moment 91% of the total area under forest in North Macedonia is managed whereas the largest part (93%) is treated as productive forest. In practice, the silvicultural system applies clear-cutting in oak forest, and, as a result, bare lands and even-aged forests are created while old-growth forests are reduced in size (Trajkov et al. 2016, Kolevska et al. 2017). In North Macedonia, ca. 1% of forests are logged annually by national forestry service (Kolevska et al. 2017, State Statistics Office 2018), while illegal logging is considerably high, with additional 30% to legal wood extraction. According to the National action plan for fight against desertification in the Republic of Macedonia (2017), in the 2000–2012 period, a decrease of 35,000 ha (4%) of forest area had occurred based on analysis of CORINE land cover. Therefore, the quality of the appropriate habitat is continuously reducing, posing a major threat to maintenance of a stable fungal population. Тhe thermophilous deciduous woodland (Annex I HD G1.7) in North Macedonia, according to the latest Biodiversity Strategy (2018), is categorised in the group of habitats having the highest intensity of threat, due to clearcutting and fires. Moreover, vast areas of the newly-formed bare lands in the lower oak belt have been planted with invasive alien species, such as Cupressus sempervirens, C. arizonica, Robinia pseudoacacia or Pinus nigra. An assessment should also be made of the impact that these activities have on fungal populations. Decline in health of forest stands, due to diseases on Quercus spp. with varying degrees of intensity, have been reported (DPRS 2019). Diseases of oak stands are primarily caused by Euproctis chrysorrhoe L., Lymantria dispar L. and species of the family Tortricidae.

Besides the exploitation of forest, the habitat is under pressure of excavation of raw minerals such as limestone, gypsum or marble. In the period 1999-2014 more than 140 permissions for exploitation of this type of materials have been issued and the number have considerably increased in the following years (Spatial planning agency Annual Report 2015, 2017, 2018, 2019), leading to additional deprivation of the possible sites for distribution of the species.

The loss and degradation of habitat triggered by clear-cutting, exploitation of minerals and by infrastructure development pose the highest threat. Forest fires are also common in thermophilous oak woodlands.

Thus, the suitable habitat for Rubroboletus dupainii has a very small distribution area.

At the only site, extensive use of the forest in the recent years has been noticed, and in some parts bare land is created due to clear-cuttings. Near the site a quarry for limestone has been built.

Conservation actions

Conservation actions

Conservation needed: The already known location must be conserved and strictly protected against utilization of the ectomycorrhizal partner or land use. Revitalisation of the degraded area at the sole site must be performed with recruitment of native oak species. An action plan aiming to minimise the negative impact of the limestone quarry should be completed. Plan for long-term management is essential to maintain an appropriate habitat.

Due to the type of silvicultural management of oak forest (Trajkov et al. 2016), in order to maintain a good habitat quality in the country, it is vital to constitute forest reserves, to designate woodland key biotopes and practise oak recruitment. At places of logging activities, instead of clear-cutting, trees of various age should be left on site. Reforestation in the lower oak belt with alien tree species rather than oak should not be applied.

Research needed: Regular monitoring on an annual basis at the established site, coupled with field research at potential sites in order to explore the distribution and dynamics of occurrence of Rubroboletus dupainii. Precise assessment of the state of thermophilous oak forests in the country is necessary, and designing of an appropriate forest management policy for maintenance of a suitable habitat.

It is advisable to digitize and regularly update forest inventories and forestry plans. There is a necessity of habitat map elaboration.

Bibliography

Bibliography

Corriol, G. (Coord.). 2014. Liste rouge des champignons de Midi-Pyrénées. Conservatoire botanique national des Pyrénées et de Midi-Pyrénées. Midi-Pyrénées, pp. 20, France.

Dahlberg, A. and Mueller, G.M. 2011. Applying IUCN red-listing criteria for assessing and reporting on the conservation status of fungal species. Fungal Ecology 4(2): 147-162.

Diagnostic Prognostic Reporting Service of Republic of Macedonia (DPRS). 2019. Report on the state of plant diseases and pests in natural and newly established forest plantations in the Republic of Macedonia. Ministry of Agriculture, Forestry and Water Economy – Sector for Forestry, pp. 89, Skopje.

Fraiture, A and Otto, P (eds). 2015. Distribution, ecology & status of 51 macromycetes in Europe. Results of the ECCF Mapping Programme. Botanic Garden Meise, Meise.

Index Fungorum Partnership. 2020. Index Fungorum. Available at: http://www.indexfungorum.org.

Ivančević, B., Matavuly, М. and Karaman, М. 2012. Fungi (mushrooms and lichens) in Serbian legislation. Biologia Serbica 34(1-2): 19-35.

Kolevska, D.D., Blinkov, I., Trajkov, P. and Maletić, V. 2017. Reforestation in Macedonia: History, current practice and future perspectives. Reforesta 3: 155-184. DOI:https://dx.doi.org/10.21750/REFOR.3.13.37

Lizon, P. and members of the Slovak Mycological Society. 2001. Red List of Slovak Fungi – draft. Bratislava, Slovakia.

Ministry of Environment and Physical Planning. 2017. National Action Plan for Combating Desertification in the Republic of Macedonia. Support to the Republic of Macedonia for the development of a National Action Plan in line with the 10-year Strategy of the United Nations Convention to Combat Desertification (UNCCD) and the Convention reporting process by UNEP. Ministry of Environment and Physical Planning of the Republic of Macedonia, Skopje.

Ministry of Environment and Physical Planning. 2018. National biodiversity strategy and action plan: for the period 2018–2023. Support to the Republic of Macedonia for revision of national biodiversity strategy and action plan and development of the fifth national report to the convention on biodiversity. Ministry of environment and physical planning, Skopje.

Peev, D., Petrova, A.S., Anchev, M., Temniskova, D., Denchev, C.M., Ganeva, A., Gussev, C. and Vladimirov, V. (eds). 2015. Red Data Book of the Republic of Bulgaria. Vol. 1. Plants and Fungi. Sofia.

Perini, C. and Gonçalves, S.C. 2019. Rubroboletus dupainii. The IUCN Red List of Threatened Species 2019: e.T70402507A70402516. Available at: https://dx.doi.org/10.2305/IUCN.UK.2019-3.RLTS.T70402507A70402516.en. (Accessed: 12 May 2020).

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Senn-Irlet, B., Bieri, G. and Egli, S. 2007. Rote Liste der gefahrdeten Grosspilze der Schweiz. BAFU, WSL, pp. 92, Bern.

Spatial Planning Agency. 2015. Annual report for implementation of the spatial plan of the Republic of Macedonia for 2014. Ministry of Environment and Spatial Planning, pp. 303, Skopje.

Spatial Planning Agency. 2017. Annual report for implementation of the spatial plan of the Republic of Macedonia for 2015-2016. Ministry of Environment and Spatial Planning, pp. 267, Skopje.

Spatial Planning Agency. 2018. Annual report for implementation of the spatial plan of the Republic of Macedonia for 2017. Ministry of Environment and Spatial Planning, pp. 172, Skopje.

Spatial Planning Agency. 2019. Annual report for implementation of the spatial plan of the Republic of Macedonia for 2018. Ministry of Environment and Spatial Planning, pp. 183, Skopje.

State Statistical Office. 2018. MakStat database. Available at: http://makstat.stat.gov.mk/PXWeb/pxweb/mk/MakStat/MakStat__Zemjodelstvo__Sumarstvo. (Accessed: 13 March 2020).

Sugny, D., Beirnaert, P., Billot, A., Caillet, M. & M., Chevrolet, J.P., Galliot, L., Herbert, R. and Moyne, G. 2013. Liste rouge des champignons supérieurs de Franche-Comté. Publication commune Fédération Mycologique de l’Est, Conservatoire National Botanique de Franche-Comté et Société Botanique de Franche-Comté, pp. 114, LUNÉVILLE, imprimerie PARADIS.

Tkalčec, Z., Mešić, A., Matočec, N. and Kušan, I. 2008. Red book of Croatian Fungi. Ministry of Culture, State Institute for Nature Protection, Zagreb.

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Venturella, G., Altobelli, E., Bernicchia, A., Di Piazza, S., Donnini, D., Gargano, M.L., Gorjòn, S.P., Granito, V.M., Lantieri, A., Lunghini, D., Montemartini, A., Padovan, F., Pavarino, M., Pecoraro, L., Perini, C., Rana, G., Ripa, C., Salerni, E., Savino, E., Tomei, P.E., Vizzini, A., Zambonelli, A. and Zotti, M. 2011. Fungal biodiversity and in situ conservation in Italy. Plant Biosystems 145(4): 950–957. http://dx.doi.org/10.1080/11263504.2011.633115