In the context of climate change, where sustainable management and the development of increasingly limited resources are involved, the study of fungi is essential, as they are one of the pioneers in the colonization of ecosystems and indicators of the health of the ecosystems in which they live. Each type of vegetation has its own fungal community, which changes according to age, the state of health of the stands and site management [1] . According to the same author, mycotrophic species promote ecosystem regeneration with a strong positive correlation between plant and fungal biodiversity. Because of their ecology and the remarkable morphogenetic adaptations they display, polypores have long been of interest to many scientists, ever since the pioneering work of [2] and [3] . Ecologically, lignivorous polypores are the main agents of decomposition of woody matter, along with insects. They have developed nutritional and biological strategies to colonize the different ecological niches present and colonize the whole range of substrates: stems, dead or living trunks, living lianas or the root system of trees [4] . Most polypore taxa have a tropical distribution [5] [6] . Unfortunately, the first scientific data available on this fungal group in tropical Africa was compiled by European mycologists. Among these mycologists are Leif Ryvarden [7] [8] [9] ; Cony Decock [10] [11] and recently in Central Africa Alphonse Balezi in Congo [12] [13] and Prudence Yombiyeni in Gabon [14] . In West Africa, work on polypores has been made in Benin by Olou [15] and in Burkina Faso by Nankoné Samson [16] [17] and [18] .

The aim of this study is to provide scientific information on the diversity and taxonomy of lignivorous parasitic polypores in the vegetation of the village of Tin in the province of Kénédougou (Orodara).

Tin Village, located about 12 km from Orodara on the Orodara-Djigouèra road, is in the department of Orodara, capital of the province of Kenedougou ( Figure 1 ) in the upper basins region of western Burkina Faso. It is located at 11˚04'922'' North and 04˚57'139'' West, at an altitude of 472 m. The indigenous people are the Siamus, who live in community with the Peulhs and other minority ethnic groups.Average annual rainfall varies from 900 to 1200 mm of water. The vegetation on the site is of the wooded savannah to tree type [19] , with Parkia biglobosa, Vitellaria paradoxa, Khaya senegalensis, Butyrospermum parkii, Terminalia sp. There are also numerous orchards of Mangifera indica, Anacardium

occidentale and a wide range of citrus trees.

Our inventory work on phytopathogenic macromycetes took place over two rainy seasons, i.e. from July to September 2018 and 2019. The survey was carried out in the Tin landscape, an area of 40,000 m² (i.e. 1000 m long by 40 m wide). A random sampling plan was used to collect all the basidiomes encountered. These mycological outings consisted of walking through the plant formation concerned and collecting all the fungi that had developed on the crown, trunk or stem and on the twigs of the woody species. Each basidiome encountered was labelled, photographed using a Canon DS126621 camera, the fleeting characteristics noted, the geographical coordinates recorded using a Garmin 64S Global Positioning System (GPS) and the host plants identified. Finally, using a machete, the basidiome has been detached from its substrate and wrapped in aluminium foil.

Once at the base camp, each carpophore was described macroscopically, followed by a technical photograph of the different parts of the cap and/or stipe.

Once the specimens had been described and photographed, they were dried in a Dorrex electric desiccator for 24 hours. The exsiccata were stored in hermetically sealed mini-grip bags with their labels and sent to the Phytopathology and Tropical Mycology laboratory at Joseph KI-ZERBO University for further analysis.

The description of macroscopic characteristics consisted of describing the morphological characteristics of the basidiome in the fresh state. It took into account the growth habit, habitus, shape, consistency, margin of the carpophore, coating of the carpophore and stipe as well as their dimensions (diameter, thickness and length), characteristics of the hymenophore (tubes, spines and pores). This description was based on the macromycete description sheet of [21] , which was simplified and adapted for the description of polypores. The characters described enabled an initial discrimination between genera. The microscopic description concerned the exsiccata. An optical microscope fitted with a NIKON H 550 S drawing tube was used. Depending on the consistency of the carpophore, different sectioning techniques were used: a longitudinal section was made through the hymenium for the search of the silks, hyphae and basidia, and a scraping of the hymenial surface was made for the search of basidiospores. The resulting cuts were deposited in a drop of 10% KOH to swell the structures. Ammoniacal Congo red (1%) was then used to color cell walls such as generative and skeletal hyphae, basidia and cystids. A few drops of Melzer’s reagent were used to check the amyloidicity of the basidiospores.

Each of the elements observed was drawn at the highest magnification (G = 1000×) of the microscope, then measured (length and width) using a micro-meter (µm) incorporated into one of the eyepieces and the ratio (Q) of spores (Q = L/l) was calculated using the Excel spreadsheet. This allowed the shape of basidiospores to be determined using the scale [22] .

In ecology, according to [23] , the study of diversity is a central property and is based on taxonomic richness (the number of taxa) and the relative abundance of each taxon within the community. Therefore, the specific richness corresponds to the number of species, and measures of richness and diversity are intimately linked to the definition of a species. Inventory work on plant-parasitic polypores has enabled us to list 44 fungal samples classified in two (2) orders: the Hymenochaetales and the Polyporales, in three families: the Hymenochaetaceae, the Ganodermataceae and the Polyporaceae, and in eight genera, the most important of which are: Phellinus and Ganoderma. From the different descriptions, eight species have been described, all of which are identified as parasites of trunks and/or branches of living woody species. This reinforces the assertion of [24] attesting to a great diversity of polypores in tropical forests because of their great richness in floristic composition. The dominant abundance of fungal species of the Hymenochaetaceae family on the Tin site could be explained by the climate, rainfall and vegetation type of the western part of the country. Indeed, the author suggests that a wide variety of wood resources (botanical diversity, substrate diversity) could result in a large number of ecological niches for polypores. The results of Ryvarden’s work [8] confirm the theory that the wide distribution of lignicolous macrofungi in the tropics is due to its high plant diversity. Furthermore, [25] found that the type of vegetation was one of the factors linked to the appearance of polypore communities in forests. If we take into account the ratio of number of species/forest area. According to [26] the host plant would be identified as a factor in the production of fruiting bodies of plant-parasitic fungi, due to the need for certain nutrients to form sporophores. Thus, Parkia biglobosa, Anogeissus leiocarpus, Mangifera indica and Annona senegalensis would be sensitive and favourable hosts for the development of plant-parasitic polypores of the Hymenochaetaceae family. It should also be noted that polypores often have a wide range of host plants, which is confirmed by the results of work by [13] , which show that Inonotus pachyphloeus and Phellinus calcitratus are also parasites of Bikinia sp. (Caesalpiniaceae), Phellinopsis pinicola with Berlinia grandifolia, Piliostigma thonningui, Acacia dudgeoni and even Acacia polymorpha. However, most of the woody plants parasitised were old strains, which corroborates the results of [27] , which showed that fungal species of the Hymenochaetaceae family were parasites of ageing Caesalpiniaceae. They conclude by saying that macrofungi of the genera Inonotus and Phellinus would be indicators of the ageing state of plant formations. In short, it could be said that the presence of these plant-parasitic polypores constitute a pathological problem for the vegetation in the village of Tin, which, because the ageing of the woody species combined with human activity and the right climatic conditions, encourages the development of lignicolous parasitic polypores. Parkia biglobosa, which is an important utility plant, seems to be the most attacked. It is therefore urgent that phytosanitary measures are found to effectively combat these parasitic hymenochaetaceae, which are becoming a significant threat to the survival of certain woody species.

This study, which took place in the vegetation of the village of Tin, identified eight species of polypore, all of which are parasites of the trunks and/or branches of certain ligneous trees. The results of the work of numerous authors have shown that the presence of these lignicolous macro-fungi attests to the ageing of plant formations. Among the woody species identified as host plants, Pakia biglobosaseems to be the preferred host plant for these hymenochaetaceae parasites. The importance of this plant for the local population is well established, hence the urgent need to put in place appropriate phytosanitary measures to preserve these ageing trees in the short term, and to consider the renewal of these woody species in the medium term through reforestation campaigns.