Abstract
Clathrus archeri is a saprophytic fungus native to the southern hemisphere which was introduced in Europe in the early twentieth century. Although it is naturalized in most regions of Central Europe, in Romania it is considered rather a rare species because it has been identified in only a few localities. Because of the rapid expansion of its range throughout Europe some authors assign this species an invasive potential. The objective of the paper was to identify both the potential distribution area and the potential suitable habitats for expansion in Romania and to highlight the environmental variables driving the probability of its occurrence. The maximum entropy model approach implemented in Maxent was used to model the species? potential distribution. The results highlighted altitude, snow cover length, the mean temperature of the driest quarter, and precipitation in the coldest quarter as the most important predictors of species? potential distribution in Romania. The map of the predicted distribution showed that the highest probability of occurrence for this species is in the mountainous and adjacent areas, while the map of habitat suitability confirmed that the best environmental conditions are in the Carpathians, while the most unfavourable are in the south-eastern regions of the country.
Highlights
Clathrus archeri (Berk.) Dring is one of the two species of the genus Clathrus in Romania
According to the jackknife test and the selection of variables depending on their significance, the most important predictors of C. archeri distribution in Romania are altitude (ALT), snow cover length (SL), the mean temperature of the driest quarter, and precipitation in the coldest quarter
In Romania, both the driest quarter and the coldest quarter are between December and February, indicating winter time
Summary
Clathrus archeri (Berk.) Dring is one of the two species of the genus Clathrus in Romania (the other species is Clathrus ruber). Clathrus archeri is a saprophytic fungus native to the southern hemisphere, Australia and New Zealand (Parent & Thoen 1986; Pietras et al 2016). It was introduced in Europe in the early twentieth century (first record in 1914, France, Vosges Mountains) and gradually spread to several European countries (Stebel 2015). According to the same authors, this species is naturalized in most regions of Central Europe It was reported in other European countries with a warmer climate, from the southern and western parts of the continent.
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