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Article

Ecological Factors Influencing the Occurrence of Macrofungi from Eastern Mountainous Areas to the Central Plains of Jilin Province, China

1
Engineering Research Centre of Edible and Medicinal Fungi, Ministry of Education, Jilin Agricultural University, Changchun 130118, China
2
School of Life Science, Northeast Normal University, Changchun 130024, China
3
Joint Laboratory of International Cooperation in Modern Agricultural Technology, Ministry of Education, Jilin Agricultural University, Changchun 130118, China
4
China Mycological Valley (Hefei), Hefei 231100, China
*
Authors to whom correspondence should be addressed.
J. Fungi 2022, 8(8), 871; https://doi.org/10.3390/jof8080871
Submission received: 22 July 2022 / Accepted: 16 August 2022 / Published: 18 August 2022

Abstract

:
Macrofungi are essential in forest ecological functioning. Their distribution and diversity are primarily impacted by vegetation, topography, and environmental factors, such as precipitation and temperature. However, the composition and topographical changes of the macrofungi between the eastern mountainous area and central plains of Jilin Province are currently unknown. For this study, we selected six investigational sites representing three different topographical research sites in Jilin Province to assess macrofungal diversity, and applied a quadrat sampling method. Macro- and micro-morphological characteristics combined with the molecular method were used to identify the collected macrofungi. Meanwhile, selected meteorological data were obtained for statistical analysis. As a result, 691 species were identified, of which Agarics were the most common, accounting for 60.23%, while the Cantharelloid fungi were the least common (0.91%). Furthermore, most of the shared genera (species) were saprophytic. The α diversity showed that the species diversity and richness in Longwan National Forest Park (B2) were the highest at the genus level. The mycorrhizal macrofungi proportion revealed that Quanshuidong Forest Farm (A1) was the healthiest. Finally, species composition similarity decreased with the transition from mountainous to hilly plains. We concluded that the occurrence of macrofungi was most influenced by vegetation. The air humidity, precipitation, and wind velocity were also found to significantly impact the occurrence of macrofungi. Finally, the mycorrhizal:saprophytic ratios and species similarity decreased with the transition from the mountainous area to the plains. The results presented here help elucidate the macrofungi composition and their relationship with environmental factors and topography in Jilin Province, which is crucial for sustainable utilization and future conservation.

1. Introduction

Human beings have discovered and utilized macrofungi throughout history with an awareness of the essential role in forest ecology. Macrofungi form mycorrhizal symbioses with host plants to promote the absorbance of substances, such as mineral elements and water. They also improve the tolerance of host plants to heavy metals, promote the survival and growth of afforestation and seedlings, and improve the diversity and stability of plants in the forest ecosystem. The comprehensive effects of macrofungi on the forest ecosystem are mainly manifested by increasing the plant–soil connections, improving the soil structure, promoting soil microorganisms, enhancing the function of plant organs, resisting antagonistic plant root disease pathogens, and degrading wood and other substances [1,2,3,4]. Saprotrophic macrofungi are also involved in the material cycle and energy flow, such as decomposing fallen timber and dead wood into other substances, such as lignin, cellulose, and hemicellulose [5,6], finally converted into glucose, fructose, etc.
Forests, as a habitat, are essential for the growth of macrofungi. Studies have shown that canopy openness, vegetation structure, and tree species richness strongly influence the occurrence of macrofungal functional groups [7]. Plant size, tree density, herb richness, and evenness could also affect the macrofungi composition [8]. Wood rotting fungi are strongly associated with tree species and the degree of wood decay [9]. Additionally, the species richness of macrofungi is also significantly related to forest management [10,11,12].
Topography is an abiotic factor that affects macrofungi community structures, as spatial eigenvectors—for example, slope—strongly connect with macrofungi occurrence [13]. Topography, more importantly, forms micro-habitats, thus creating differences in the key factors such as temperature, air humidity, and light, which affect the occurrence of macrofungi.
Furthermore, the occurrence and growth of macrofungi are closely related to environmental factors. For example, ectomycorrhizal macrofungi (EM fungi) are closely associated with their host plants, as Tuo et al. revealed the quantity of EM fungi in Wunvfeng National Forest Park, China, was positively correlated with the occurrence of Quercus mongolica [6]. Humidity is another critical factor, and Trudell et al. characterized the epigeous macrofungi communities in two old-growth conifer forests with a high level of similarity in their dominant tree species and proposed that the differences between the macrofungi communities were primarily related to the disparities in ecosystem moisture [14]. In addition, pH [15], soil temperature [16], and organic matter content [17,18] could also affect the occurrence of macrofungi.
There are apparent differences in the topography of Jilin Province. The terrain inclines from southeast to northwest and could be divided into two significant landforms: the eastern mountainous area and the central-western plains. The eastern mountainous area comprises the middle part of Mt. Changbai and its branches [19], accounting for 33% of the total area; hills account for 6% of the area. Due to the unique natural geographical environment and meteorological conditions, Jilin Province has become one of China’s biodiversity hotspots. New macrofungi species have been discovered here, including Cortinarius laccariphyllus Y. Li and M.L. Xie; Cortinarius neotorvus Y. Li, M.L. Xie, and T.Z. Wei [20]; Cordyceps changchunensis J.J. Hu, Bo Zhang, and Y. Li; Cordyceps changbaiensis J.J. Hu, Bo Zhang, and Y. Li; and Cordyceps jingyuetanensis J.J. Hu, Bo Zhang, and Y. Li [21]. However, the macrofungi distribution patterns and the relationship with the environmental factors are currently unclear.
With this study, we aim to understand the species composition and macrofungal distribution in the central and eastern areas of Jilin Province and analyze the relationship between their occurrence and environmental factors. In addition, we analyze the changes in the macrofungi composition about to topography.

2. Materials and Methods

2.1. Introduction of Investigation Site

Jilin Province has a temperate continental monsoon climate, with four distinct seasons, rain and heat in the same season, noticeable seasonal changes, and regional differences in temperature and precipitation. The average temperature is below −11 °C in the winter and above 23 °C in the summer [22,23,24], and the average annual precipitation is 400–600 mm [25,26,27]. However, precipitation significantly differs between seasons and regions, as 80% is concentrated in the summer, and the eastern area is the richest.
Six representative investigation sites were selected to assess the macrofungi resources and analyze the relationships between macrofungi occurrence in eastern Jilin Province, China, in detail (Figure 1 and Figure 2 and Table 1). These sites are Mt. Changbai area (A)—Quanshuidong Forest Farm (A1) and Lushuihe National Forest Park (A2); Mt. Changbai branches, Mt. Laoyeling branch (B)—Shengli River Forest Farm (B1) and Mt. Longgang branch—Longwan National Forest Park (B2); and low hilly plain areas (C)—Zuojia Region (C1) and Jingyuetan National Forest Park (C2). The investigation also aimed to improve our understanding of the composition transitions from the eastern to central regions, which cause changes in topography, vegetation, precipitation, and temperature.
(1)
Quanshuidong Forest Farm (A1)
Quanshuidong Forest Farm, located in Helong City, Jilin Province, belongs to the mid-temperate monsoonal semi-humid climate zone. The annual average temperature is 5.6 °C, and the effective accumulated temperature at 10 °C is 2534.0 °C. The average yearly precipitation is 573.6 mm, and the frost-free period is approximately 138 days [28].
(2)
Lushuihe National Forest Park (A2)
Lushuihe National Forest Park, located in Fusong County, Baishang City, Jilin Province, belongs to the temperate monsoon climate. The annual average temperature is 2.9 °C, and the effective accumulated temperature at 10 °C is 2606.9 °C. The average yearly precipitation is 894 mm, and the frost-free period is approximately 110 days [29].
(3)
Laoyeling Branch—Shengli River Forest Farm (B1)
Mt. Laoyeling belongs to the Mt. Changbai Systems and is in the northeast–southwest direction, 800–1000 m above sea level in Jilin Province, with a relative height of approximately 500 m. The landforms are mainly low and middle mountains, with narrow valleys between the mountains. Volcanoes and lava flows are widely distributed in this area [27].
Shengli River Forest Farm has a temperate continental climate with an average annual temperature of 3.8 °C, an average annual rainfall of 633.7 mm, and a frost-free period of 110–130 days.
(4)
Longgang Mountain Branch—Longwan National Forest Park (B2)
Longwan National Forest Park is in the middle section of Mt. Longgang in Huinan County, Jilin Province, with an average sea level of 880 m. It has a northern temperate continental monsoon climate. The annual average temperature is 4.8 °C, the minimum temperature is −17 °C, and the maximum monthly average temperature is 22.4 °C. The sufficient accumulated temperature at 10 °C is 2728 °C. The average annual precipitation is 837.9 mm, ranging from 436.5 to 987.2 mm. The maximum daily precipitation is 124.2 mm, concentrated from June to August, with an average yearly frost-free period of 138 days and an average sunshine time of 2296 h [30].
(5)
Zuojia Region (C1)
The Zuojia area, Jilin Province, belongs to the hilly plain areas of Mt. Changbai. It has a continental climate with temperate monsoons and often experiences Siberian cold waves, with changeable weather and distinct seasons. The annual average temperature is 5.6 °C, and the effective accumulated temperature at 10 °C is 2779.8 °C. The average yearly precipitation is 679 mm, the average annual evaporation is 1200 mm, and the frost-free period is approximately 120 days [31,32,33].
(6)
Jingyuetan National Forest Park (C2)
Jingyuetan National Forest Park is in the transitional zone from the eastern mountain area to the western grasslands of Jilin Province. It belongs to the hill areas of Mt. Changbai. The elevation is between 245.8 and 371.6 m above sea level. The climate is temperate semi-dry, early, and semi-humid monsoon with four distinct seasons. The annual average temperature is 6.1 °C. The average annual precipitation is 577.3 mm. The rainy season is mainly concentrated in July and August, as it accounts for 67% of the annual precipitation, the annual evaporation is 1392.5 mm, and there is a frost-free period of 145 d [34].

2.2. Macrofungi Investigation

(1)
Investigation
In this study, four plots were selected at each investigation site in which three quadrats of 10 m × 10 m [35] were set in parallel at each plot, and each plot was numbered with a distance of 300 m, applied with a quadrat sampling method.
(2)
Specimen collection and recording
Specimens were mainly collected from July to September at every investigation site. The specimens were photographed in situ. The habitat, altitude, soil characteristics, and nearby trees were recorded. The size of basidiomata was measured when fresh, and features such as striations, hygrophanous, and squama were noted (Figure 3). After examining and describing the fresh macroscopic characters, the specimens were dried in an electric drier at 45–50 °C. All the collected specimens had conspicuous basidiomata.
(3)
Specimen identification
The dried specimens were rehydrated in 94% ethanol for microscopic examination, then mounted in 3% potassium hydroxide (KOH), 1% Congo red, and Melzer’s reagent; they were then examined with a Zeiss Axiolab A1 microscope (Carl Zeiss, Jena, Germany) at magnifications up to 1000×. All measurements were taken from the sections mounted in 1% Congo red. A minimum of 40 spores, 20 basidia/asci, 20 cystidia, etc., were measured from at least two different fruiting bodies for each specimen [36]. When combined with the macroscopic characteristics, the classification status of the specimens was determined by referring to literature and monographs [37]. For some species, we also sequenced, and the sequences have been deposited in GenBank (GenBank accession numbers: ON683416–ON683495). The taxonomic status of all species is referenced in the Index Fungorum [38]. The specimens examined were deposited in the Herbarium of Mycology of Jilin Agricultural University (HMJAU).
(4)
Data collection
The meteorological data—average temperature (T), average relative humidity (RH), average monthly precipitation (P), average wind speed, and accumulated temperature from July to September (AT)—were downloaded from the China meteorological data network [39]. The soil type and representative forest type data were obtained from the Chinese Academy of Sciences (Table 2) [40].

2.3. Data Analysis

Two alpha diversity indices, the Simpson diversity index [41] and the Shannon–Wiener index [42], were calculated at the genus level for each investigation site to analyze the community composition of the macrofungi. The Shannon index (H′) reflected the diversity of the community species. The Simpson index (D) reflected the probability of two individuals being randomly selected from the same sample, and these two individuals are from the same class.
The compositions of the macrofungi at Mt. Changbai (A), the transitional zone (B), and the plain hilly area (C) were compared by calculating the similarity coefficient (S) [43] and generating a complex heatmap [44]. The macrofungi compositions between Mt. Changbai and Mt. Laoyeling branch and Mt. Longgang Branch were also compared.
The diversity index formulae were as follows:
H = P i ln ( P i )
D = 1 P i 2
S = 2 a b + c × 100
where Pi is the proportion of species i to the total number of individuals of all species in the plot, a is the number of genera shared by the two places, and b and c are the genera that appear in the same place.
According to the Atlas of Chinese Macrofungal Resources [37], identified species were divided into eight categories: Larger Ascomycete, Agarics, Polyporoid, Hyonaceous and Thelephoroid fungi (PHT fungi), Cantharelloid fungi, Gasteroid fungi, Jelly fungi, Coral fungi, and Boletes.
The identified genera were summarized in an Excel table. Then, we specified a value of 0/1 for each genus shown at each investigation site (0 means that the genus did not appear at the investigation site). Originpro 2019 (OriginLab, Northampton, USA) was used to analyze common genera. Dominant family (number of species more than ten of the family) and dominant genus (number of species more than five of the genera) of each investigation site were counted [45]. Moreover, the species numbers per family (genera) at all six investigation sites were statistics, the top ten families (genera) were shown, and the bubble matrix was drowned.
The software Canoco 5.0 (Micro-computer Power, Ithaca, NY, USA) [46] fits and analyzes the relationship between macrofungi species and the environmental factors at six investigation sites. Log (n + 1) was used to reduce meteorological data quality and balance the vast differences among the various factors. The quadrat × species matrix and the quadrat × environment matrix were established. Two-dimensional sorting and canonical correspondence analysis (CCA) of macrofungi and environmental factors in six different vegetation types were conducted.

3. Results

3.1. Composition Characteristics of the Macrofungi

In this study, genera with more than four species were chosen from the six investigation sites for analysis. Site A1 included the most identified families and species among six investigation sites, while site B2 had the fewest (Figure 4). General overview, Russula Pers., Pholiota (Fr.) P. Kumm., and Mycena (Pers.) Roussel, etc., were the most common genera recorded. Taxa belonging to Russula and Mycena were the most common at site A1; Pholiota and Polyporus were the most common ones at site A2; Russula, Pholiota, and Hygrophorus Fr. were the most reported genera at site B1; Russula and Amanita Pers were the most recorded at site B2; Russula, Suillus Gray, and Pholiota were the most reported at site C1; Russula, Suillus, and Agaricus L., were the most common genera at site C2. Overall, the most reported one is Russula.

3.2. Shared Genera (Species) Analysis

A total of 691 species of macrofungi, belonging to 258 genera and 81 families, were identified (Table A1). There were 23 genera—including Ampulloclitocybe Redhead, Lutzoni, Moncalvo and Vilgalys, Cortinarius, and Pleurotus—identified at all six investigation sites (Figure 5A).
Furthermore, 11 species, such as Ampulloclitocybe clavipes (Pers.) Redhead, Lutzoni, Moncalvo and Vilgalys, Daldinia concentrica (Bolton) Ces. and De Not., and Ganoderma applanatum (Pers.) Pat., co-occurred at each survey site (Figure 5B). Site A1 has the most endemic species, while site B2 has the fewest.

3.3. Macrofungi Composition Types Analysis

According to the Atlas of Chinese Macrofungal Resources [37], the macrofungi species were divided into eight statistical categories. Agarics were the most common, accounting for 60.23% of the total, followed by PHT fungi, accounting for 16.50%. In contrast, Jelly fungi and Cantharelloid fungi were rarely reported, accounting for 2.06% and 0.91%, respectively (Figure 6A).
The statistical analysis of each investigation site (Figure 6B) showed that Agarics and PHT fungi were predominant at sites A1, A2, B1, B2, C1, and C2, while Agarics and Jelly fungi were the most common at site B2. Coral fungi and Cantharelloid fungi were rarely reported at sites A1, A2, and B2. Jelly fungi and Cantharelloid fungi were seldom reported at sites B1, C1, and C2. In summary, Cantharelloid fungi were rare in all investigations, while the compositions of macrofungi at six investigation sites were vastly different.

3.4. Ecological Characteristics of Macrofungi

According to the reference [6] and FUNGuild [47], the numbers of mycorrhizal macrofungi and saprophytic macrofungi were counted. The proportion of mycorrhizal macrofungi at site A1 was the highest (0.47), indicating that the forest structure at this site was the healthiest and the most stable. While the proportion was the lowest at site C1 (Table 3).

3.5. Analysis of α Diversity

The α diversity at six investigation sites was analyzed (Figure 7). The summary statistics from the Simpson diversity index for site B2 were significantly higher than those from the other five investigation sites. This result indicated that site B2 had the richest species diversity at the genus level and the most uniform distribution of species quantity (Figure 7A). The Shannon–Wiener index results also indicated that the diversity at site B2 was the highest, and the species were the richest (Figure 6B).

3.6. Analysis of Dominant Families (Genera)

According to the identification results, 81 families were recorded. The top ten families were Russulaceae, Tricholomataceae, Agaricaceae, etc., successively, containing 43.54% of the total species (Table 4). There were 24 families with only one species, accounting for 29.63%. The dominant families at each investigation site are shown in Figure 8A.
A total of 258 genera were reported in this study, among which the top ten genera were Mycena (Pers.) Roussel, Cortinarius (Pers.) Gray, Lactarius Pers., etc., accounting for 22.46% (Table 4). There were 137 genera with only one species, accounting for 53.10%. The dominant genera are shown in Figure 8B.

3.7. Relationships between Macrofungi and Environmental Factors

At first, the number of macrofungi collected from May to October at the three investigation sites was analyzed statistically. The results showed that they mainly arose from July to September, with minimal presence in May, June, and October (Figure 9).
Secondly, the relationship between macrofungi and environmental facts—air humidity, precipitation, and temperature were also analyzed. Macrofungi occurrence was positively correlated with air humidity (Figure 10). When air humidity was higher, larger numbers of macrofungi were shown from July to September. Precipitation from May to October was positively correlated with macrofungi occurrence with a lag period (Figure 11).
Then, the relationship between the average temperature from May to October and macrofungi occurrence was also analyzed. The results showed that macrofungi occurrence at sites A1 (Figure 12A) and B2 (Figure 12B) was positively correlated with air temperature, and there was a relative lag period. However, numerous macrofungi occurred in September at site C2 (Figure 12C), while the monthly average temperature was significantly lower than from June to July. Further analysis of the meteorological data shows that the daily temperature difference at site C2 was significant in September, stimulating macrofungi formation.
At last, a canonical correspondence analysis (CCA) was performed on the genera with the top 50% species numbers recorded at the six investigation sites. Five environmental factors—adequate accumulated temperature (AT), monthly mean air temperature from (T), mean humidity (RH), mean precipitation (P), and mean wind speed from July to September (S)—were selected for CCA. The results (Figure 13) showed that all samples were roughly separated into six groups according to their corresponding locations. Eigenvalue axis 1 is higher than axis 2, with cumulative contributions of 32.70% and 28.50%, respectively. The selected environmental factors were found to impact the macrofungi occurrence. Of all the established ecological factors, the mean humidity from July to September, mean precipitation from July to September, and mean wind speed from July to September were the most significant factors.

3.8. Analysis of Flora Diversity

The six investigation sites were divided into three groups: Mt. Changbai area (A), containing Quanshuidong Forest Farm (A1) and Lushuihe National Forest Park (A2); Mt. Changbai Branch (B), comprising the Mt. Longgang Branch (Longwan National Forest Park, B1) and the Mt. Laoyeling Branch (Shengli Forest Farm, B2); and plain low hilly areas (C), encompassing the Zuojia Region (C1) and Jingyuetan National Forest Park (C2). The macrofungi composition was found to change when the mountainous region transited to the plains and low hills, and this was determined by calculating the similarity coefficient (s). The similarity decreased from 42.06% to 39.95% (Table 5).
Simultaneously, the macrofungi compositions of Mt. Changbai, its Laoyeling Branch (B1), and the Mt. Longgang Branch (B2) were compared. The similarity between Mt. Changbai and Laoyeling Branch (B1) was 37.23%, higher than the Mt. Longgang Branch.
The top 30 genera were selected to analyze the speciation differences (Figure 14). The composition of site C1 was the most similar to site C2, followed by site B2 and site B1, and site A was the least similar, which was consistent with the results for the similarity coefficient. The similarity of the species composition in Mt. Changbai Branch was lower than that in the plain low hilly area.
Substantial differences were seen in forming distinct genera among the six sites. The number of species in each genus was generally higher for area A and lower for site B2.

4. Discussion

4.1. The Influence of Environmental Factors on Macrofungi Occurrence

CCA at the genus level of recorded macrofungi at six investigation sites showed that the mean humidity, mean precipitation, and mean wind speed from July to September were the most significant environmental factors influencing the occurrence and distribution of macrofungi.
The effect of wind speed on macrofungi is integrated and multifaceted. The most direct impact is an expansion of the dispersal of the spores range, promoting species dispersal and affecting the macrofungi’s community structure by promoting the formation of dominant populations and reducing the macrofungi species richness within the same plant community [48]. Wind speed will also affect the oxygen content of the plant–macrofungi community. The high oxygen content will influence the oxygen content of soil [49], thus promoting hyphae respiration—the more energy released, the more promotion of mycelium growth [50]. Oxygen content will also affect the fruiting body morphogenesis, and elevated carbon dioxide will result in the formation of deformed mushrooms, thus affecting the macrofungi growth (e.g., the height of fruiting bodies lower than average) [51,52]. Wind speed will also affect soil moisture and air humidity [53]. From a positive perspective, water evaporation and transpiration will increase air humidity and adjust soil and air temperature, which benefits fruiting body formation. However, if the soil moisture evaporates excessively during spore germination and vegetative hyphal growth, excessive evaporation of the soil moisture will inhibit spore germination and promote hyphal reproductive growth or dormancy [54,55,56]. Furthermore, soil dryness caused by high winds may be a reason that macrofungi become gasteroid.
Precipitation will increase the soil water content, enabling resting spores to obtain sufficient water levels. For spores with thick walls, water immersion is essential. Sufficient soaking softens the walls, triggering enzymes hydrolysis of the spore’s peptidoglycan cortex, enabling the mycelium to germinate more efficiently [57]. Water immersion will also dissolve the substances that inhibit spore germination into the water and release dormancy [58]. Furthermore, water can promote spore respiration and sugar decomposition, provide energy for growth activities, and stimulate spores to secrete various enzymes to destroy cell wall structures [59]. With the gradual temperature increase, the spores were found to absorb enough water to germinate gradually. The suitable temperature and humidity conditions were sufficient for the mycelium to grow in large quantities, laying the foundations for macrofungi occurrence [60,61]. However, this phenomenon depends on vital mechanisms of the spore, for dead spores do not swell, and absorption varies with the viability of the spore [62]. The swelling of spores is usually more than twice its original size [63], and with further germination, the protoplasm volume can sometimes increase more than ten times.
Relative humidity mainly affects the dispersal of spores. If the air humidity is too high, the weight/volume will also increase, thus reducing the dispersal range of spores [64]. The evidence shows that the RH had no direct influence on the growth of macrofungi [53]. If water is available on the surface, macrofungi may grow at deficient air humidity levels [65,66]. RH may also influence the growth of mycelia. Excessively high RH would slow down or inhibit mycelium growth [67].
Mushrooms also arise from primordia that their formation and differentiation are influenced by environmental factors such as precipitation and temperature. From 1993 to 2007, Krebs et al. [68] found that mushroom production could be predicted by summer rainfall, in Yukon, the mushroom production is positively correlated with precipitation. Low humidity will slow down the growth rate during primordia formation [69]. The temperature is also another critical factor. The formation of some mushroom’s primordia requires low-temperature stimulation, such as Flammlina filiformis (Z.W. Ge, X.B. Liu, and Zhu L. Yang) P.M. Wang, Y.C. Dai, E. Horak, and Zhu L. Yang. The diverse climate types and environments allow different macrofungi to specialize and thrive [70].

4.2. The Influence of Vegetation on Macrofungi Occurrence

The Mt. Longgang and Mt. Laoyeling branches both belong to Mt. Changbai. However, the species richness in the Longwan National Forest Park (B2) was found to be higher than that at Mt. Changbai (A) and its Mt. Laoyeling branch (B1). This phenomenon may be due to the differences in their vegetation [71]. Mt. Changbai and its Mt. Laoyeling Branch are mainly covered by coniferous trees, including Pinus spp., Picea spp., etc. In contrast, Longgang Branch (Longwan National Forest Park, B2) is primarily covered with broadleaf mixed forests, such as Quercus mongolica and some pine forests. Macrofungi can show preferences for broadleaf or coniferous trees, vegetation, or substrate specificity might have contributed to the evolution of macrofungi [11,70]. Our result (Figure 6) shows that the typical composition of recorded macrofungi varied in proportion across the six investigation sites. Jelly fungi, for example, at site B2 reached 13%; however, they were only 1–3% at the other investigation sites. Furthermore, deadwood fungi prefer different deadwood characteristics (host species, decay, etc.), and thus, species composition changes can occur about these characteristics [72]. It is evidenced that macrofungi species are usually more abundant in broadleaf forests than in coniferous forests [11]. According to our calculations, the wood and litter saprotroph macrofungi reached 51.7% at site B2, while sites A1, A2, and B1 were 50.3%, 47.9%, and 46.3%, respectively. In addition, plant community composition determines understory light availability, humidity, and litter composition [73]. At the same time, many macrofungal species have host associations with particular plant species; for example, Tuo et al. revealed that the quantity of EM fungi in Wunvfeng National Forest Park, China, was positively correlated with the amount of Q. mongolica [6]. Based on our results, site A1 had the highest proportion of EM fungi at 45.78% and site B2 had the lowest at 28.57% among Mt. Changbai and its branch sites. The balance between mycorrhizal macrofungi and saprophytic macrofungi is a reference to forest conditions [74,75,76,77]. In a healthy forest, the number of mycorrhizal macrofungi often exceeds the number of saprophytic macrofungi [78,79]. Moreover, the plant community constitutes an abiotic factor of crucial importance for fungal composition [80,81]. However, some studies have demonstrated that the contribution of plant communities to the impact of macrofungi communities is only 1–10% [82]. Therefore, the effects of plant communities on macrofungi require further investigation.

4.3. The Influence of Topography on Macrofungi Occurrence

The ratio of mycorrhizal macrofungi to saprophytic macrofungi decreased with the transition from the eastern mountains to the central plains. Unlike light or soil properties, the topography is an indirect environmental variable [83,84]. Topography is considered an essential driver of micro-habitat diversity in forest ecosystems [85,86], as different topographies result in various micro-habitats. Different micro-habitats can favor the occurrence of a wider variety of macrofungal species [84], thus leading to different macrofungi compositions, which we observed in our results. In our findings, the proportion of macrofungal composition types varied across six survey sites (Figure 6). Moreover, the species numbers for each genus shifted with topography (Figure 14). For example, the Lepiota and Geastrum species were most common at site C2; however, they were considered rare at the other sites.
Different macrofungi compositions eventually result in variations in species similarity. Species similarity decreased with the transition from the mountainous area to the plains area in this investigation. Furthermore, the similarity between Mt. Changbai and its Laoyeling Branch (Shengli Forestry Farm, B1) was higher than between Mt. Changbai and the Mt. Longgang branch (Longwan National Forest Park, B2). Based on the comparison of the representative vegetation and soil types of the three areas, the representative forest types and soil types in the Laoyeling Branch and Mt. Changbai area were highly similar, and it is speculated that the occurrence of macrofungi is not only related to vegetation but also closely related to soil types. Soil type influenced spore density and the percentage of mycorrhizal colonization of roots, where high spore density was not necessarily connected with intensive mycorrhizal development [87].

5. Conclusions

The occurrence of macrofungi is closely related to vegetation. By comparing sites B1 and B2, we found that the macrofungal abundance increased with increasing proportions of broadleaf trees, and specific genera were present at every survey site. Moreover, the nutritional patterns of co-occurring genera (species) were analyzed, most of which were saprophytic macrofungi.
The mycorrhizal:saprophytic ratios decreased with the transition from mountains to plains. The mycorrhizal:saprophytic ratios were consistently higher in the northeast than the southwest sites in the Mt. Changbai region and its branches.
Species similarity decreased with the transition from the mountainous area to the plains area; in addition, the species similarity between the Laoyeling Branch (B1) and Mt. Changbai (A) is higher than that between the Mt. Longgang Branch (B2) and Mt. Changbai (A).
The main environmental factors affecting macrofungi occurrence from the eastern mountains to the central plains of Jilin Province are the air humidity (RH), precipitation (P), and wind speed (S) from July to September. Our canonical correspondence analysis reveals the importance of wind speed in macrofungal occurrence.

Author Contributions

Conceptualization, Y.L. and B.Z.; experimental design and methodology, Y.L., B.Z., J.-J.H. and Y.-L.T.; performance of practical work, J.-J.H. and G.-P.Z.; statistical analyses, J.-J.H., Y.-L.T., Z.-X.Q. and L.Y.; validation, J.-J.H. and B.Z.; writing—original draft preparation, J.-J.H.; writing—review and editing, B.Z.; supervision, Y.L. and B.Z.; project administration, B.Z.; funding acquisition, B.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the National Natural Science Foundation of China (31970020), the Scientific and Technological Tackling Plan for the Key Fields of Xinjiang Production and Construction Corps (2021AB004), the Key Project on R&D of the Ministry of Science and Technology (2019YFD1001905-33), the Modern Agroindustry Technology Research System (CARS20), Research on the Creation of Excellent Edible Mushroom Resources and High Quality & Efficient Ecological Cultivation Technology in Jiangxi Province (20212BBF61002), Modern Agricultural Scientific Research Collaborative Innovation Special Project (JXXTCXBSJJ202212), and the “111” program (D17014).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We would like to give great thanks to Ye Ding, Xu Wang, Yue-Qu Chen, Shu-Rong Wang, and Jian-Rui Wang for their specimen collection. The authors would also like to give great thanks to the National Meteorological Science Data Center of China, the Resource Discipline Innovation Platform of China, for providing the data.

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A

Table A1. Macrofungi list of collected species in three different landforms from Jilin Province.
Table A1. Macrofungi list of collected species in three different landforms from Jilin Province.
Scientific NameDistributionNutritional ModeEconomic ValueCategoriesGenBank Accession Number
A1A2B1B2C1C2
Abortiporus biennis (Bull.) Singer SSMedicinalPHT fungi
Agaricus abruptibulbus Peck SSEdible, PoisonousAgaricsON683434
Agaricus arvensis Schaeff. SSEdible, MedicinalAgarics
Agaricus bresadolanus Bohus SSEdible, MedicinalAgarics
Agaricus campestris L. SSEdible, MedicinalAgarics
Agaricus comtulus Fr. SSEdibleAgarics
Agaricus micromegethus Peck SSEdible, MedicinalAgarics
Agaricus moelleri Wasser SSEdible, PoisonousAgaricsON683435
Agaricus perrarus Fr. SSOthersAgarics
Agaricus placomyces Peck SSEdible, MedicinalAgarics
Agaricus purpurellus F.H. Møller SSOthersAgarics
Agaricus silvaticus Schaeff. SSEdible, MedicinalAgarics
Agaricus silvicolae-similis Bohus and Locsmándi SSOthersAgarics
Agaricus subrufescens Peck SSEdible, MedicinalAgarics
Agaricus subrutilescens (Kauffman) Hotson and D.E. Stuntz SSEdible, MedicinalAgarics
Agaricus sylvaticus Schaeff. SSEdible, MedicinalAgarics
Agrocybe pediades (Fr.) Fayod SSEdible, MedicinalAgarics
Agrocybe praecox (Pers.) Fayod SSEdible, MedicinalAgaricsON683416
Aleuria aurantia (Pers.) Fuckel SSEdible, Medicinal, PoisonousLarger Ascomycetes
Aleurodiscus stereoides Yasuda SSOthersPHT fungi
Amanita ceciliae (Berk. and Broome) Bas EMOthersAgaricsON683421
Amanita fulva Fr. EMOthersAgarics
Amanita hemibapha (Berk. and Broome) Sacc. EMEdible, MedicinalAgarics
Amanita imazekii T. Oda, C. Tanaka and Tsuda EMEdibleAgarics
Amanita longistriata S. Imai EMPoisonousAgarics
Amanita nivalis Grev. EMEdibleAgarics
Amanita pantherina (DC.) Krombh EMPoisonousAgarics
Amanita phalloides (Vaill. ex Fr.) Link EMOthersAgaricsON683436
Amanita porphyria Alb. and Schwein. EMOthersAgaricsON683437
Amanita spreta (Peck) Sacc. EMOthersAgarics
Amanita subjunquillea S. Imai EMPoisonousAgaricsON683438
Amanita vaginata (Bull.) Lam. EMEdible, Medicinal, PoisonousAgaricsON683439
Amanita virosa Secr. EMMedicinal, PoisonousAgarics
Amanitopsis fulva (Fr.) W.G. Sm. EMOthersAgarics
Ampulloclitocybe clavipes (Pers.) Redhead, Lutzoni, Moncalvo and VilgalysLSEdible, Medicinal, PoisonousAgarics
Apioperdon pyriforme (Schaeff.) Vizzini EMEdible, MedicinalGasteroid fungi
Armillaria borealis Marxm. and Korhonen WSEdible, MedicinalAgarics
Armillaria cepistipes Velen. WSOthersAgarics
Armillaria gallica Marxm. and Romagn. WSEdible, MedicinalAgaricsON683440
Armillaria mellea (Vahl) P. Kumm. WSEdible, MedicinalAgarics
Armillaria ostoyae (Romagn.) Herink WSEdible, MedicinalAgarics
Armillaria sinapina Bérubé and Dessur. WSEdible, MedicinalAgaricsON683422
Armillariella mellea (Vahl) P. Karst. WSEdible, MedicinalAgarics
Artomyces pyxidatus (Pers.) Jülich WSEdibleCoral fungi
Ascocoryne cylichnium (Tul.) Korf WSOthersLarger Ascomycetes
Astraeus hygrometricus (Pers.) Morgan SSMedicinalGasteroid fungi
Atheniella adonis (Bull.) Redhead, Moncalvo, Vilgalys, Desjardin, and B.A. Perry LSOthersAgarics
Auricularia cornea Ehrenb. WSEdible, MedicinalJelly fungi
Auricularia heimuer F. Wu, B.K. Cui, and Y.C. Dai WSEdible, MedicinalJelly fungi
Auricularia mesenterica (Dicks.) Pers. WSOthersJelly fungi
Auricularia nigricans (Sw.) Birkebak, Looney and Sánchez-García WSEdible, MedicinalJelly fungi
Auriscalpium vulgare Gray WSOthersPHT fungi
Baeospora myriadophylla (Peck) Singer LSOthersAgarics
Bisporella sulfurina (Quél.) S.E. Carp. WSOthersLarger Ascomycetes
Bjerkandera adusta (Willd.) P. Karst. WSMedicinalPHT fungi
Bolbitius vitellinus (Pers.) Fr. SSOthersAgarics
Bolbitius vitellinus (Pers.) Fr. EMOthersBoletes
Boletinellus merulioides (Schwein.) Murrill EMOthersBoletes
Boletus edulis Bull. EMEdibleBoletes
Boletus subtomentosus J.A. Palmer EMOthersBoletes
Boletus subvelutipes Peck EMOthersBoletes
Boletus yunnanensis W.F. Chiu EMPoisonousBoletes
Bovista pusilla (Batsch) Pers. SSOthersGasteroid fungi
Bovista pusilliformis (Kreisel) Kreisel SSOthersGasteroid fungi
Bulgaria inquinans (Pers.) Fr. WSEdible, Medicinal, PoisonousLarger Ascomycetes
Byssomerulius corium (Pers.) Parmasto WSOthersPHT fungi
Calocera cornea (Batsch) Fr. WSOthersJelly fungi
Calocera viscosa (Pers.) Fr. WSMedicinal, PoisonousJelly fungi
Calocybe gambosa (Fr.) Donk SSEdible, MedicinalAgarics
Calocybe ionides (Bull.) Donk SSEdibleAgarics
Calvatia craniiformis (Schwein.) Fr. ex De Toni SSEdible, MedicinalGasteroid fungi
Calvatia lilacina (Mont. and Berk.) Henn. SSEdible, MedicinalGasteroid fungi
Calvatia tatrensis Hollós SSMedicinalGasteroid fungi
Camarophyllus pratensis (Pers.) P. Kumm. SSOthersAgarics
Campanella tristis (G. Stev.) Segedin WSOthersAgarics
Cantharellus cibarius Fr. EMEdible, MedicinalCantharelloid fungiON683495
Cantharellus minor Peck EMEdible, MedicinalCantharelloid fungi
Cerioporus squamosus (Huds.) Quél. WSMedicinalPHT fungi
Cerioporus varius (Pers.) Zmitr. and Kovalenko WSEdiblePHT fungi
Ceriporia tarda (Berk.) Ginns WSOthersPHT fungi
Cheilymenia coprinaria (Cooke) Boud. WSOthersLarger Ascomycetes
Chlorociboria aeruginascens (Nyl.) Kanouse WSOthersLarger Ascomycetes
Chroogomphus purpurascens (Lj.N. Vassiljeva) M.M. Nazarova EMEdibleBoletes
Chroogomphus roseolus Y.C. Li and Zhu L. Yang EMEdible, MedicinalBoletes
Chroogomphus rutilus (Schaeff.) O.K. Mill. EMEdible, MedicinalBoletesON683423
Chroogomphus tomentosus (Murrill) O.K. Mill. EMOthersBoletes
Chrysomphalina aurantiaca (Peck) Redhead WSOthersAgarics
Clavaria fragilis Holmsk. SSMedicinal, PoisonousCoral fungi
Clavaria vermicularis Sw. SSEdibleCoral fungi
Clavariadelphus pistillaris (L.) Donk LSEdible, PoisonousCoral fungiON683441
Clavicorona pyxidata (Pers.) Doty WSOthersCoral fungi
Clavulina coralloides (L.) J. Schröt. LSEdibleCoral fungiON683424
Clavulinopsis corniculata (Schaeff.) Corner LSEdibleCoral fungi
Clavulinopsis fusiformis (Sowerby) Corner LSEdibleCoral fungi
Clavulinopsis helvola (Pers.) Corner LSEdibleCoral fungi
Clitocybe infundibuliformis (Schaeff.) Quél. LSEdible, MedicinalAgarics
Clitocybe nebularis (Batsch) P. Kumm. LSEdible, MedicinalAgarics
Clitocybe odora (Bull.) P. Kumm. LSEdible, MedicinalAgaricsON683417
Clitocybe phyllophila (Pers.) P. Kumm. LSPoisonousAgarics
Clitopilus prunulus (Scop.) P. Kumm. LSEdibleAgarics
Collybia nivea (Mont.) Dennis SSOthersAgarics
Collybiopsis confluens (Pers.) R.H. Petersen SSOthersAgaricsON683418
Collybiopsis peronata (Bolton) R.H. Petersen SSOthersAgarics
Coltricia cinnamomea (Jacq.) Murrill SSOthersPHT fungi
Coltricia perennis (L.) Murrill SSOthersPHT fungi
Connopus acervatus (Fr.) K.W. Hughes, Mather and R.H. Petersen SSEdibleAgarics
Conocybe lactea (J.E. Lange) Métrod SSMedicinalAgarics
Conocybe tenera (Schaeff.) Kühner SSPoisonousAgarics
Coprinellus disseminatus (Pers.) J.E. Lange SSPoisonousAgarics
Coprinellus micaceus (Bull.) Vilgalys, Hopple and Jacq. Johnson SSMedicinal, PoisonousAgarics
Coprinopsis atramentaria (Bull.) Redhead, Vilgalys and Moncalvo SSEdible, Medicinal, PoisonousAgarics
Coprinopsis cinerea (Schaeff.) Redhead, Vilgalys and Moncalvo SSMedicinalAgarics
Coprinopsis insignis (Peck) Redhead, Vilgalys & Moncalvo SSMedicinalAgarics
Coprinopsis lagopus (Fr.) Redhead, Vilgalys and Moncalvo SSMedicinalAgarics
Coprinopsis picacea (Bull.) Redhead, Vilgalys and Moncalvo SSPoisonousAgarics
Coprinus comatus (O.F. Müll.) Pers. DSEdible, Medicinal, PoisonousAgarics
Coprinus micaceus (Bull.) Fr. DSMedicinal, PoisonousAgarics
Coprinus plicatilis (Curtis) Fr. DSOthersAgarics
Coprinus sterquilinus (Fr.) Fr. DSMedicinalAgarics
Cordyceps farinosa (Holmsk.) Kepler, B. Shrestha and Spatafora EIOthersLarger Ascomycetes
Cordyceps militaris (L.) Fr. EIEdible, MedicinalLarger Ascomycetes
Cordyceps nutans Pat. EIOthersLarger Ascomycetes
Coriolopsis gallica (Fr.) Ryvarden WSOthersPHT fungi
Cortinarius alboviolaceus (Pers.) Fr. EMEdibleAgarics
Cortinarius armillatus (Fr.) Fr. EMOthersAgarics
Cortinarius bovinus Fr. EMEdible, MedicinalAgarics
Cortinarius caerulescens (Schaeff.) Fr. EMOthersAgarics
Cortinarius callochrous (Pers.) Gray EMEdible, PoisonousAgarics
Cortinarius caperatus (Pers.) Fr. EMEdible, MedicinalAgarics
Cortinarius cinnamomeus (L.) Gray EMEdible, Medicinal, PoisonousAgarics
Cortinarius collinitus (Sowerby) Gray EMEdible, MedicinalAgarics
Cortinarius colymbadinus Fr. EMOthersAgarics
Cortinarius elatior Fr. EMOthersAgarics
Cortinarius galeroides Hongo EMOthersAgarics
Cortinarius lilacinus Peck EMPoisonousAgarics
Cortinarius longipes Peck EMOthersAgarics
Cortinarius multiformis Fr. EMEdibleAgarics
Cortinarius orellanus Fr. EMPoisonousAgarics
Cortinarius purpurascens Fr. EMEdibleAgaricsON683425
Cortinarius sanguineus (Wulfen) Gray EMMedicinal, PoisonousAgarics
Cortinarius trivialis J.E. Lange EMEdible, PoisonousAgarics
Cotylidia diaphana (Cooke) Lentz LSOthersPHT fungi
Cotylidia komabensis (Henn.) D.A. Reid LSOthersPHT fungi
Craterellus undulatus (Pers.) E. Campo and Papetti EMEdibleAgarics
Crepidotus applanatus (Pers.) P. Kumm. WSOthersAgarics
Crepidotus badiofloccosus S. Imai WSOthersAgarics
Crepidotus betulae Murrill WSOthersAgarics
Crepidotus brasiliensis Rick WSMedicinalAgarics
Crepidotus epibryus (Fr.) Quél. WSOthersAgarics
Crepidotus fulvotomentosus (Peck) Peck WSOthersAgarics
Crepidotus herbarum Sacc. WSOthersAgarics
Crepidotus mollis (Schaeff.) Staude WSOthersAgarics
Crepidotus nephrode (Berk. and M.A. Curtis) Sacc. WSOthersAgarics
Crepidotus nephrodes (Berk. and M.A. Curtis) Sacc. WSOthersAgarics
Crepidotus palmularis (Berk. and M.A. Curtis) Sacc. WSOthersAgarics
Crepidotus sulphurinus Imazeki and Toki WSOthersAgarics
Crepidotus variabilis (Pers.) P. Kumm. WSOthersAgarics
Crinipellis stipitaria (Fr.) Pat. LSOthersAgarics
Cuphophyllus pratensis (Pers.) Bon SSEdibleAgaricsON683442
Cuphophyllus virgineus (Wulfen) Kovalenko SSOthersAgarics
Cyanosporus caesius (Schrad.) McGinty WSOthersPHT fungi
Cyathus stercoreus (Schwein.) De Toni WSMedicinalGasteroid fungi
Cyathus striatus Willd. WSMedicinalGasteroid fungi
Cyclocybe cylindracea (DC.) Vizzini and Angelini SSEdible, MedicinalAgarics
Cyclocybe erebia (Fr.) Vizzini and Matheny SSEdible, MedicinalAgarics
Cystoderma amianthinum (Scop.) Fayod SSEdibleAgarics
Cystoderma fallax A.H. Sm. and Singer SSEdibleAgarics
Cystodermella granulosa (Batsch) Harmaja SSEdibleAgarics
Dacrymyces chrysospermus Berk. and M.A. Curtis WSOthersJelly fungi
Dacrymyces palmatus Bres. WSMedicinalJelly fungiON683443
Dacryopinax spathularia (Schwein.) G.W. Martin WSOthersJelly fungi
Daedalea dickinsii Yasuda WSMedicinalPHT fungiON683444
Daedaleopsis confragosa (Bolton) J. Schröt. WSOthersPHT fungi
Daedaleopsis tricolor (Bull.) Bondartsev and Singer WSMedicinalPHT fungiON683426
Daldinia concentrica (Bolton) Ces. and De Not.WSMedicinal, PoisonousLarger Ascomycetes
Daldinia grandis Child WSOthersLarger Ascomycetes
Deconica coprophila (Bull.) P. Karst. DSPoisonousAgarics
Deconica merdaria (Fr.) Noordel. DSPoisonousAgarics
Desarmillaria tabescens (Scop.) R.A. Koch and Aime SSEdible, Medicinal, PoisonousAgarics
Descolea flavoannulata (Lj.N. Vassiljeva) E. Horak SSEdibleAgarics
Dumontinia tuberosa (Bull.) L.M. Kohn SSOthersLarger Ascomycetes
Entoloma abortivum (Berk. and M.A. Curtis) Donk SSEdible, MedicinalAgarics
Entoloma albipes Hesler SSOthersAgarics
Entoloma chamaecyparidis (Hongo) Hongo SSOthersAgarics
Entoloma clypeatum (L.) P. Kumm. SSMedicinal, PoisonousAgarics
Entoloma japonicum (Hongo) Hongo and Izawa SSOthersAgarics
Entoloma lividum Quél. SSOthersAgarics
Entoloma murinipes (Murrill) Hesler SSOthersAgarics
Entoloma murrillii Hesler SSOthersAgarics
Entoloma politum (Pers.) Noordel. SSOthersAgarics
Entoloma rhodopolium (Fr.) P. Kumm. SSMedicinal, PoisonousAgarics
Entoloma sinuatum (Bull.) P. Kumm. SSMedicinal, PoisonousAgarics
Entoloma speculum (Fr.) Quél. SSOthersAgarics
Entoloma umbilicatum Dennis SSOthersAgarics
Entonaema liquescens Möller WSOthersLarger Ascomycetes
Exidia glandulosa (Bull.) Fr. WSEdible, PoisonousJelly fungi
Flammulaster erinaceellus (Peck) Watling WSOthersAgarics
Flammulina filiformis (Z.W. Ge, X.B. Liu, and Zhu L. Yang) P.M. Wang, Y.C. Dai, E. Horak, and Zhu L. YangWSEdibleAgarics
Fomes fomentarius (L.) Fr. WSMedicinalPHT fungiON683445
Fomitopsis betulina (Bull.) B.K. Cui, M.L. Han, and Y.C. Dai WSMedicinalPHT fungi
Fomitopsis officinalis (Vill.) Bondartsev and Singer WSMedicinalPHT fungi
Fomitopsis pinicola (Sw.) P. Karst. WSMedicinalPHT fungiON683446
Galerina helvoliceps (Berk. and M.A. Curtis) Singer WSPoisonousPHT fungi
Galerina marginata (Batsch) Kühner SSPoisonousPHT fungi
Galerina vittaeformis (Fr.) Singer SSOthersAgarics
Galiella amurensis (Lj.N. Vassiljeva) Raitv. SSOthersLarger Ascomycetes
Ganoderma applanatum (Pers.) Pat.WSMedicinalPHT fungi
Ganoderma tsugae Murrill WSMedicinalPHT fungi
Geastrum fimbriatum Fr. LSMedicinalGasteroid fungi
Geastrum pectinatum Pers. LSOthersGasteroid fungi
Geastrum saccatum Fr. LSMedicinalGasteroid fungi
Geastrum triplex Jungh. LSMedicinalGasteroid fungi
Gerronema albidum (Fr.) Singer SSEdibleAgarics
Gliophorus psittacinu (Schaeff.) Herink SSEdible, PoisonousAgarics
Gloeophyllum sepiarium (Wulfen) P. Karst. WSMedicinalPHT fungi
Gloeophyllum subferrugineum (Berk.) Bondartsev and Singer WSOthersPHT fungi
Gloeophyllum trabeum (Pers.) Murrill WSMedicinalPHT fungi
Gloeostereum incarnatum S. Ito and S. Imai WSEdible, MedicinalPHT fungi
Gomphidius maculatus (Scop.) Fr. EMEdibleBoletes
Gomphus clavatus (Pers.) Gray EMEdible, MedicinalCantharelloid fungi
Guepinia helvelloides (DC.) Fr. SSEdibleJelly fungi
Gymnopilus aeruginosus (Peck) Singer WSOthersAgarics
Gymnopilus junonius (Fr.) P.D. Orton WSOthersAgarics
Gymnopilus liquiritiae (Pers.) P. Karst. WSMedicinal, PoisonousAgarics
Gymnopilus penetrans (Fr.) Murrill WSPoisonousAgaricsON683447
Gymnopus alkalivirens (Singer) Halling LSOthersAgarics
Gymnopus androsaceus (L.) J.L. Mata and R.H. Petersen LSMedicinalAgarics
Gymnopus dryophilus (Bull.) MurrilLSEdible, PoisonousAgaricsON683448
Gymnopus erythropus (Pers.) Antonín, Halling and Noordel. LSEdibleAgaricsON683449
Gymnopus fusipes (Bull.) Gray LSEdibleAgarics
Gymnopus ocior (Pers.) Antonín and Noordel. LSEdibleAgarics
Gymnopus polyphyllus (Peck) Halling LSOthersAgarics
Harrya chromipes (Frost) Halling, Nuhn, Osmundson and Manfr. Binder EMOthersBoletes
Hebeloma hiemale Bres. SSOthersAgarics
Hebeloma radicosum (Bull.) Ricken SSEdible, PoisonousAgarics
Helvella atra J. König SSEdibleLarger Ascomycetes
Helvella crispa (Scop.) Fr.SSEdible, PoisonousLarger Ascomycetes
Helvella elastica Bull. SSEdible, PoisonousLarger Ascomycetes
Helvella ephippium Lév. SSEdibleLarger Ascomycetes
Helvella lacunosa Afzel. SSEdible, MedicinalLarger Ascomycetes
Hemistropharia albocrenulata (Peck) Jacobsson and E. Larss. WSEdible, PoisonousAgarics
Hericium coralloides (Scop.) Pers. WSEdible, MedicinalPHT fungi
Hericium erinaceus (Bull.) Pers. WSEdible, MedicinalPHT fungiON683494
Heterobasidion insulare (Murrill) Ryvarden WSOthersPHT fungi
Hohenbuehelia reniformis (G. Mey.) Singer WSEdibleAgarics
Hohenbuehelia serotina (Pers.) Singer WSOthersAgarics
Hortiboletus rubellus (Krombh.) Simonini, Vizzini and Gelardi EMEdible, MedicinalBoletes
Humaria hemisphaerica (F.H. Wigg.) Fuckel SSOthersLarger Ascomycetes
Hydnum repandum L. EMEdible, MedicinalPHT fungi
Hygrocybe ceracea (Sowerby) P. Kumm. SSEdibleAgarics
Hygrocybe chlorophana (Fr.) Wünsche SSEdibleAgarics
Hygrocybe coccinea (Schaeff.) P. Kumm. SSEdibleAgarics
Hygrocybe conica (Schaeff.) P. Kumm. SSMedicinal, PoisonousAgarics
Hygrocybe flavescens (Kauffman) Singer SSPoisonousAgarics
Hygrocybe marchii (Bres.) Singer SSOthersAgarics
Hygrocybe miniata (Fr.) P. Kumm. SSEdibleAgaricsON683450
Hygrophorus chrysodon (Batsch) Fr. SSEdibleAgarics
Hygrophorus eburneus (Bull.) Fr. SSEdibleAgarics
Hygrophorus laurae Morgan SSOthersAgarics
Hygrophorus lucorum Kalchbr. SSEdible, MedicinalAgarics
Hygrophorus occidentalis A.H. Sm. and Hesler SSOthersAgarics
Hygrophorus olivaceo-albus (Fr.) Fr. SSEdibleAgarics
Hygrophorus piceae Kühner SSOthersAgarics
Hygrophorus pseudochrysaspis Hesler and A.H. Sm. SSOthersAgarics
Hygrophorus russula (Schaeff. ex Fr.) Kauffman SSEdibleAgaricsON683451
Hymenochaete adusta (Lév.) Har. and Pat. WSOthersPHT fungi
Hymenochaete corrugata (Fr.) Lév. WSOthersPHT fungi
Hymenochaete xerantica (Berk.) S.H. He and Y.C. Dai WSOthersPHT fungi
Hymenopellis radicata (Relhan) R.H. Petersen SSOthersAgarics
Hymenoscyphus fructigenus (Bull.) Gray WSOthersLarger Ascomycetes
Hypholoma capnoides (Fr.) P. Kumm. WSMedicinal, PoisonousAgarics
Hypholoma fasciculare (Huds.) P. Kumm. WSMedicinal, PoisonousAgarics
Hypholoma lateritium (Schaeff.) P. Kumm. WSPoisonousAgarics
Hypsizygus marmoreus (Peck) H.E. Bigelow WSOthersAgaricsON683452
Hypsizygus ulmarius (Bull.) Redhead WSEdible, MedicinalAgarics
Infundibulicybe geotropa (Bull.) Harmaja SSEdible, Medicinal, PoisonousAgarics
Infundibulicybe gibba (Pers.) P. Kumm. LSEdibleAgaricsON683453
Inocybe asterospora Quél. EMPoisonousAgarics
Inocybe calamistrata (Fr.) Gillet EMPoisonousAgarics
Inocybe changbaiensis T. Bau and Y.G. Fan EMOthersAgarics
Inocybe cookei Bres. EMPoisonousAgarics
Inocybe earleana Kauffma EMOthersAgarics
Inocybe euviolacea E. Ludw. EMOthersAgarics
Inocybe fulvella Bres. EMOthersAgarics
Inocybe geophylla P. Kumm. EMPoisonousAgarics
Inocybe napipes J.E. Lange EMPoisonousAgarics
Inocybe praetervisa Quél. EMPoisonousAgarics
Inocybe subalbidodisca Stangl and J. Veselský EMOthersAgarics
Inocybe umbrinella Bres. EMOthersAgarics
Inonotus hispidus (Bull.) P. Karst. WSMedicinalPHT fungiON683454
Inonotus obliquus (Fr.) Pilát WSMedicinalPHT fungi
Inosperma calamistratum (Fr.) Matheny and Esteve-Rav. LSOthersAgarics
Irpex lacteus (Fr.) Fr. WSOthersPHT fungi
Isaria japonica Yasuda EIOthersLarger Ascomycetes
Junghuhnia nitida (Pers.) Ryvarden WSEdiblePHT fungi
Kuehneromyces mutabilis (Schaeff.) Singer and A.H. Sm. WSEdibleAgaricsON683455
Laccaria alba Zhu L. Yang and Lan Wang EMEdibleAgaricsON683456
Laccaria amethystea (Bull.) Murrill EMOthersAgaricsON683457
Laccaria amethystina Cooke EMOthersAgarics
Laccaria laccata (Scop.) Cooke EMEdible, MedicinalAgaricsON683458
Laccaria proxima (Boud.) Pat. EMOthersAgarics
Laccaria purpureobadia D.A. Reid EMOthersAgarics
Laccaria tortilis (Bolton) Cooke EMEdible, MedicinalAgaricsON683459
Lacrymaria lacrymabunda (Bull.) Pat. SSPoisonousAgarics
Lactarius acris (Bolton) Gray EMOthersAgarics
Lactarius aurantiacus (Pers.) Gray EMEdible, MedicinalAgarics
Lactarius camphoratus (Bull.) Fr. EMEdibleAgarics
Lactarius circellatus Fr. EMEdibleAgarics
Lactarius deliciosus (L.) Gray EMEdible, MedicinalAgarics
Lactarius fuliginosus (Fr.) Fr. EMEdibleAgarics
Lactarius hatsudake Nobuj. Tanaka EMEdible, MedicinalAgarics
Lactarius lignyotus Fr. EMMedicinal, PoisonousAgarics
Lactarius mitissimus (Fr.) Fr. EMOthersAgarics
Lactarius piperatus (L.) Pers. EMEdible, Medicinal, PoisonousAgarics
Lactarius subdulcis (Pers.) Gray EMEdibleAgarics
Lactarius theiogalus (Bull.) Gray EMOthersAgarics
Lactarius torminosus (Schaeff.) Pers. EMPoisonousAgarics
Lactarius trivialis (Fr.) Fr. EMOthersAgarics
Lactarius vellereus (Fr.) Fr. EMEdible, Medicinal, PoisonousAgarics
Lactarius vietus (Fr.) Fr. EMEdibleAgarics
Lactarius volemus (Fr.) Fr. EMEdible, MedicinalAgaricsON683460
Lactarius zonarius (Bull.) Fr. EMMedicinal, PoisonousAgarics
Lactifluus subpiperatus (Hongo) Verbeken EMOthersAgarics
Laetiporus cremeiporus Y. Ota and T. Hatt. WSEdible, MedicinalPHT fungi
Laetiporus montanus Černý ex Tomšovský and Jankovský WSEdiblePHT fungi
Laetiporus sulphureus (Bull.) Murrill WSEdible, MedicinalPHT fungiON683461
Leccinum chromapes (Frost) Singer EMOthersBoletes
Leccinum scabrum (Bull.) Gray EMEdible, PoisonousBoletes
Lentinellus flabelliformis (Bolton) S. Ito WSOthersAgarics
Lentinellus ursinus (Fr.) Kühner WSEdibleAgarics
Lentinula edodes (Berk.) Pegler WSEdible, MedicinalAgarics
Lentinus arcularius (Batsch) Zmitr. WSMedicinalPHT fungi
Lentinus brumalis (Pers.) Zmitr. WSEdiblePHT fungi
Lentinus elmeri Bres. WSOthersPHT fungi
Lentinus substrictus (Bolton) Zmitr. and Kovalenko WSOthersPHT fungi
Lentinus tigrinus (Bull.) Fr. WSEdible, MedicinalPHT fungi
Lenzites albida (Fr.) Fr. WSEdiblePHT fungi
Lenzites betulinus (L.) Fr. WSMedicinalPHT fungi
Lenzites repanda Fr. WSPoisonousPHT fungi
Leotia lubrica (Scop.) Pers. SSOthersLarger Ascomycetes
Lepiota brunneoincarnata Chodat and C. Martín LSPoisonousAgarics
Lepiota castanea Quél. LSPoisonousAgarics
Lepiota clypeolaria (Bull.) P. Kumm. LSPoisonousAgaricsON683462
Lepiota cristata (Bolton) P. Kumm. LSPoisonousAgarics
Lepiota erminea (Fr.) P. Kumm. LSEdibleAgarics
Lepiota felina (Pers.) P. Karst. LSOthersAgarics
Lepiota fusciceps Hongo LSOthersAgarics
Lepiota magnispora Murrill LSOthersAgarics
Lepista glaucocana (Bres.) Singer LSEdibleAgarics
Lepista irina (Fr.) H.E. Bigelow LSMedicinal, PoisonousAgarics
Lepista nuda (Bull.) CookeLSEdible, MedicinalAgaricsON683463
Lepista personata (Fr.) Cooke LSEdible, MedicinalAgarics
Lepista sordida (Schumach.) Singer LSEdible, MedicinalAgarics
Leucoagaricus leucothites (Vittad.) Wasser SSEdible, Medicinal, PoisonousAgarics
Leucoagaricus rubrotinctus (Peck) Singer SSOthersAgaricsON683464
Leucocoprinus brebissonii (Godey) Locq. SSOthersAgarics
Leucocybe candicans (Pers.) Vizzini, P. Alvarado, G. Moreno, and Consiglio SSMedicinal, PoisonousAgarics
Leucocybe connata (Schumach.) Vizzini, P. Alvarado, G. Moreno, and Consiglio SSEdible, PoisonousAgarics
Leucocybe houghtonii (W. Phillips) Halama and Pencak. SSOthersAgarics
Lopharia cinerascens (Schwein.) G. Cunn. WSOthersPHT fungi
Lycoperdon fuscum Huds. SSEdible, MedicinalGasteroid fungi
Lycoperdon mammaeforme Pers. SSOthersGasteroid fungi
Lycoperdon pedicellatum Batsch SSEdible, MedicinalGasteroid fungi
Lycoperdon perlatum Pers. SSEdible, MedicinalGasteroid fungiON683465
Lycoperdon pusillum Hedw. SSOthersGasteroid fungi
Lycoperdon pyriforme Schaeff. SSEdible, MedicinalGasteroid fungi
Lycoperdon umbrinum Pers. SSEdible, MedicinalGasteroid fungi
Lyophyllum decastes (Fr.) Singer EMEdible, MedicinalAgarics
Lysurus mokusin (L.) Fr. SSMedicinalGasteroid fungi
Macrocystidia cucumis (Pers.) Joss. SSOthersAgarics
Macrolepiota procera (Scop.) SingerSSEdible, Medicinal, PoisonousAgarics
Mallocybe terrigena (Fr.) Matheny, Vizzini, and Esteve-Rav. SSEdibleAgarics
Marasmiellus candidus (Fr.) Singer WSOthersAgarics
Marasmiellus eburneus (Theiss.) Singer WSOthersAgarics
Marasmiellus ramealis (Bull.) Singer WSMedicinalAgarics
Marasmius aurantiacus I. Hino LSEdible, MedicinalAgarics
Marasmius beniensis Singer LSOthersAgarics
Marasmius chordalis Fr. LSOthersAgarics
Marasmius cohaerens (Pers.) Cooke and Quél. LSOthersAgarics
Marasmius epiphyllus (Pers.) Fr. LSOthersAgarics
Marasmius floriceps Berk. and M.A. Curtis LSOthersAgarics
Marasmius maximus Hongo LSEdibleAgaricsON683427
Marasmius occultatiformis Antonín, Ryoo, and H.D. Shin LSOthersAgaricsON683419
Marasmius oreades (Bolton) Fr. LSEdible, MedicinalAgarics
Marasmius pallidocephalus Gilliam LSOthersAgarics
Marasmius polylepidis Dennis LSOthersAgarics
Marasmius pseudoniveus Singer LSOthersAgarics
Marasmius pulcherripes Peck LSOthersAgarics
Marasmius riparius Singer LSOthersAgarics
Marasmius rotuloides Dennis LSOthersAgarics
Marasmius sessiliaffinis Singer LSOthersAgarics
Marasmius siccus (Schwein.) Fr. LSOthersAgarics
Megacollybia platyphylla (Pers.) Kotl. and Pouzar WSOthersAgarics
Melanoleuca brevipes (Bull.) Pat. SSEdibleAgarics
Melanoleuca grammopodia (Bull.) Murrill SSEdibleAgarics
Melanoleuca melaleuca (Pers.) Murrill SSEdibleAgaricsON683466
Melanoleuca strictipes (P. Karst.) Jul. Schäff. SSEdibleAgarics
Melanoleuca stridula (Fr.) Singer SSOthersAgarics
Melanoleuca verrucipes (Fr.) Singer SSEdibleAgarics
Melastiza chateri (W.G. Sm.) Boud. SSOthersLarger Ascomycetes
Microporus affinis (Blume and T. Nees) Kuntze WSOthersPHT fungi
Microstoma floccosum (Sacc.) Raitv. WSOthersLarger Ascomycetes
Morchella conica Pers. SSEdibleLarger Ascomycetes
Morchella crassipes (Vent.) Pers. SSEdible, MedicinalLarger Ascomycetes
Morchella esculenta (L.) Pers. SSEdible, MedicinalLarger Ascomycetes
Morchella vulgaris (Pers.) Gray SSEdible, MedicinalLarger Ascomycetes
Mucidula brunneomarginata (Lj.N. Vassiljeva) R.H. Petersen WSEdibleAgarics
Mucidula mucida (Schrad.) Pat. WSOthersAgaricsON683467
Mutinus caninus (Huds.) Fr. SSPoisonousGasteroid fungi
Mycena alphitophora (Berk.) Sacc. LSOthersAgarics
Mycena collybiiformis (Murrill) Murrill LSOthersAgarics
Mycena debilis (Fr.) Quél. LSOthersAgarics
Mycena epipterygia (Scop.) Gray LSOthersAgarics
Mycena filopes (Bull.) P. Kumm. LSOthersAgarics
Mycena flavescens Velen. LSPoisonousAgarics
Mycena fuliginella A.H. Sm. LSOthersAgarics
Mycena galericulata (Scop.) Gray LSEdible, MedicinalAgaricsON683420
Mycena haematopus (Pers.) P. Kumm. LSMedicinal, PoisonousAgaricsON683468
Mycena inclinata (Fr.) Quél. LSOthersAgarics
Mycena nucleata X. He and X.D. Fang LSOthersAgarics
Mycena osmundicola J.E. Lange LSOthersAgarics
Mycena pseudoandrosacea (Bull.) Z.S. Bi LSOthersAgarics
Mycena pura (Pers.) P. Kumm.LSMedicinal, PoisonousAgaricsON683469
Mycena rosea Gramberg LSOthersAgarics
Mycena sanguinolenta (Alb. and Schwein.) P. Kumm. LSOthersAgarics
Mycena subcana A.H. Sm. LSOthersAgarics
Mycena subgracilis Métrod LSOthersAgarics
Mycoleptodonoides pergamenea (Yasuda) Aoshima and H. Furuk. WSOthersPHT fungi
Myxarium nucleatum Wallr. WSOthersLarger Ascomycetes
Naematelia aurantialba (Bandoni and M. Zang) Millanes and Wedin WSEdible, MedicinalJelly fungi
Neofavolus alveolaris (DC.) Sotome and T. Hatt. WSOthersPHT fungiON683470
Neolentinus adhaerens (Alb. and Schwein.) Redhead and Ginns WSEdible, MedicinalPHT fungi
Neolentinus cyathiformis (Schaeff.) Della Magg. and Trassin. WSOthersPHT fungi
Neolentinus lepideus (Fr.) Redhead and GinnsWSEdible, Medicinal, PoisonousPHT fungiON683471
Nidula niveotomentosa (Henn.) Lloyd WSMedicinalAgarics
Omphalina lilaceorosea Svrček and Kubička LSOthersAgarics
Omphalotus guepiniformis (Berk.) Neda WSPoisonousAgarics
Onnia tomentosa (Fr.) P. Karst. WSOthersPHT fungi
Ophiocordyceps nutans (Pat.) G.H. Sung, J.M. Sung, Hywel-Jones, and Spatafora EIMedicinalLarger Ascomycetes
Ophiocordyceps sphecocephala (Klotzsch ex Berk.) G.H. Sung, J.M. Sung, Hywel-Jones, and Spatafora EIMedicinalLarger Ascomycetes
Ossicaulis lignatilis (Pers.) Redhead and Ginns WSEdibleAgarics
Osteina undosa (Peck) Zmitr. WSOthersPHT fungi
Otidea cochleata (L.) Fuckel SSPoisonousLarger Ascomycetes
Otidea leporina (Batsch) Fuckel SSOthersLarger Ascomycetes
Oudemansiella radicata (Relhan) Singer SSOthersAgarics
Panaeolus campanulatus (L.) Quél. DSOthersAgarics
Panaeolus fimicola (Pers.) Gillet DSPoisonousAgarics
Panaeolus papilionaceus (Bull.) Quél. DSPoisonousAgarics
Panellus stipticus (Bull.) P. Karst. WSMedicinal, PoisonousAgaricsON683472
Panus conchatus (Bull.) Fr. WSEdible, MedicinalAgaricsON673473
Panus rudis Fr. WSOthersAgarics
Paralepista splendens (Pers.) Vizzini SSOthersAgarics
Paralepistopsis acromelalga (Ichimura) Vizzini SSPoisonousAgarics
Parasola plicatilis (Curtis) Redhead, Vilgalys, and Hopple SSMedicinalAgarics
Parasola leiocephala (P.D. Orton) Redhead, Vilgalys and Hopple SSOthersAgarics
Paxillus involutus (Batsch) Fr. EMMedicinal, PoisonousBoletes
Perenniporia inflexibilis (Berk.) Ryvarden WSOthersPHT fungi
Perenniporia medulla-panis (Jacq.) Donk WSOthersPHT fungi
Perenniporia subacida (Peck) Donk WSMedicinalPHT fungi
Peziza ampliata Pers. SSOthersLarger Ascomycetes
Peziza badia Pers. SSPoisonousLarger Ascomycetes
Peziza praetervisa Bres. SSOthersLarger Ascomycetes
Peziza sylvestris (Boud.) Sacc. and Traverso SSOthersLarger Ascomycetes
Peziza vesiculosa Bolton SSEdible, PoisonousLarger Ascomycetes
Phaeoclavulina abietina (Pers.) Giachini LSOthersCoral fungi
Phaeoclavulina flaccida (Fr.) Giachini LSPoisonousCoral fungi
Phaeolepiota aurea (Matt.) Maire SSEdible, Medicinal, PoisonousAgarics
Phaeolus schweinitzii (Fr.) Pat. WSMedicinalPHT fungi
Phaeotremella foliacea (Pers.) Wedin, J.C. Zamora and Millanes EMEdible, MedicinalJelly fungi
Phallus flavocostatus Kreisel SSOthersGasteroid fungiON683474
Phallus hadriani Vent. SSOthersGasteroid fungi
Phallus impudicus L. SSEdible, MedicinalGasteroid fungi
Phallus indusiatus Vent. SSOthersGasteroid fungi
Phallus rubicundus (Bosc) Fr. SSMedicinal, PoisonousGasteroid fungi
Phallus rugulosus (E. Fisch.) Lloyd SSOthersGasteroid fungi
Phellinus gilvus (Schwein.) Pat. WSOthersPHT fungi
Phellinus igniarius (L.) Quél. WSMedicinalPHT fungi
Phellodon fuligineoalbus (J.C. Schmidt) R.E. Baird WSOthersPHT fungi
Phellodon tomentosus (L.) Banker WSEdiblePHT fungi
Phillipsia domingensis (Berk.) Berk. ex Denison WSOthersLarger Ascomycetes
Phlebia tremellosa (Schrad.) Nakasone and Burds. WSMedicinalPHT fungi
Phloeomana minutula (Sacc.) Redhead WSOthersAgarics
Phloeomana speirea (Fr.) Redhead WSOthersAgarics
Pholiota adiposa (Batsch) P. Kumm. WSEdible, MedicinalAgarics
Pholiota aurivella (Batsch) P. Kumm. WSEdible, MedicinalAgarics
Pholiota flammans (Batsch) P. Kumm. WSEdible, Medicinal, PoisonousAgarics
Pholiota hiemalis A.H. Sm. and Hesler WSOthersAgarics
Pholiota lenta (Pers.) Singer WSEdible, MedicinalAgarics
Pholiota lubrica (Pers.) Singer WSEdible, Medicinal, PoisonousAgaricsON683475
Pholiota mutabilis (Schaeff.) P. Kumm. WSOthersAgarics
Pholiota spumosa (Fr.) Singer WSEdible, MedicinalAgaricsON683476
Pholiota squarrosa (Vahl) P. Kumm. WSEdible, Medicinal, PoisonousAgarics
Pholiota squarrosoides (Peck) Sacc. WSEdible, PoisonousAgaricsON683477
Pholiota subflavida (Murrill) A.H. Sm. and Hesler WSOthersAgarics
Pholiota tuberculosa (Schaeff.) P. Kumm. WSOthersAgarics
Pholiota veris A.H. Sm. and Hesler WSOthersAgarics
Pholiota vinaceobrunnea A.H. Sm. and Hesler WSOthersAgarics
Pholiota terrestris Overh. WSEdible, Medicinal, PoisonousAgarics
Phyllotopsis nidulans (Pers.) Singer WSEdibleAgarics
Physalacria lateriparies X. He and F.Z. Xue WSOthersAgarics
Picipes badius (Pers.) Zmitr. and Kovalenko WSOthersPHT fungiON683478
Picipes melanopus (Pers.) Zmitr. and Kovalenko WSOthersPHT fungi
Piptoporus betulinus (Bull.) P. Karst. WSMedicinalPHT fungi
Plectania melastoma (Sowerby) Fuckel WSOthersLarger Ascomycetes
Pleuroflammula flammea (Murrill) Singer SSOthersAgarics
Pleuroflammula multifolia (Peck) E. Horak SSOthersAgarics
Pleurotus citrinopileatus Singer WSEdible, MedicinalAgaricsON683479
Pleurotus cornucopiae (Paulet) Quél. WSEdible, MedicinalAgarics
Pleurotus corticatus (Fr.) P. Kumm. WSOthersAgarics
Pleurotus dryinus (Pers.) P. Kumm. WSEdible, MedicinalAgarics
Pleurotus limpidus (Fr.) P. Karst. WSEdibleAgarics
Pleurotus ostreatus (Jacq.) P. Kumm.WSEdible, MedicinalAgaricsON683480
Pleurotus pulmonarius (Fr.) Quél. WSEdible, MedicinalAgaricsON683481
Pleurotus spodoleucus (Fr.) Quél. WSEdible, MedicinalAgarics
Pluteus atricapillus (Batsch) Fayod WSOthersAgarics
Pluteus atromarginatus (Konrad) Kühner WSEdibleAgarics
Pluteus aurantiorugosus (Trog) Sacc. WSEdibleAgaricsON683482
Pluteus cervinus (Schaeff.) P. Kumm. WSEdibleAgarics
Pluteus depauperatus Romagn. WSOthersAgarics
Pluteus leoninus (Schaeff.) P. Kumm. WSEdibleAgarics
Pluteus nanus (Pers.) P. Kumm. WSOthersAgarics
Pluteus petasatus (Fr.) Gillet WSEdibleAgarics
Pluteus plautus (Weinm.) Gillet WSOthersAgarics
Pluteus salicinus (Pers.) P. Kumm. WSEdibleAgarics
Pluteus umbrosus (Pers.) P. Kumm. WSEdibleAgarics
Podosordaria pedunculata (Dicks.) Dennis WSOthersLarger Ascomycetes
Polyporus alveolaris (DC.) Bondartsev and Singer WSOthersPHT fungi
Polyporus badius (Pers.) Schwein. WSOthersPHT fungi
Polyporus brumalis (Pers.) Fr. WSOthersPHT fungi
Polyporus conifericola H.J. Xue and L.W. Zhou WSOthersPHT fungiON683483
Polyporus squamosus (Huds.) Fr. WSMedicinalPHT fungi
Polyporus tuberaster (Jacq. ex Pers.) Fr. WSOthersPHT fungi
Polyporus varius (Pers.) Fr. WSMedicinalPHT fungi
Polystictus unicolor Rick WSOthersPHT fungi
Polystictus versicolor (L.) Fr. WSOthersPHT fungi
Psathyrella candolleana (Fr.) Maire WSMedicinal, PoisonousAgaricsON683484
Psathyrella hydrophila (Bull.) Maire WSOthersAgarics
Psathyrella multissima (S. Imai) Hongo WSOthersAgarics
Psathyrella subnuda (P. Karst.) A.H. Sm. WSOthersAgarics
Pseudoclitocybe cyathiformis (Bull.) Singer SSEdible, MedicinalAgaricsON683485
Pseudofavolus tenuis (Fr.) G. Cunn. WSMedicinal, PoisonousPHT fungi
Pseudohydnum gelatinosum (Scop.) P. Karst. WSEdible, MedicinalJelly fungi
Pseudosperma avellaneum (Kobayasi) Matheny and Esteve-Rav. SSOthersAgarics
Pseudosperma rimosum (Bull.) Matheny and Esteve-Rav. SSOthersAgarics
Pseudosperma umbrinellum (Bres.) Matheny and Esteve-Rav. SSOthersAgarics
Pterula multifida (Chevall.) Fr. SSOthersCoral fungiON683486
Pycnoporus cinnabarinus (Jacq.) P. Karst. WSMedicinalPHT fungi
Pycnoporus sanguineus (L.) Murrill WSMedicinalPHT fungi
Radulodon copelandii (Pat.) N. Maek. WSOthersPHT fungi
Radulomyces copelandii (Pat.) Hjortstam and Spooner WSOthersPHT fungi
Ramaria apiculata (Fr.) Donk EMEdible, MedicinalCoral fungi
Ramaria botrytis (Pers.) Bourdot EMEdible, MedicinalCoral fungi
Ramaria bourdotiana Maire EMEdibleCoral fungi
Ramaria flava (Schaeff.) Quél. EMEdible, Medicinal, PoisonousCoral fungi
Ramaria formosa (Pers.) Quél. EMEdible, Medicinal, PoisonousCoral fungi
Ramaria lutea Schild EMEdibleCoral fungi
Ramaria madagascariensis (Henn.) Corner EMOthersCoral fungi
Ramaria stricta (Pers.) Quél. EMEdibleCoral fungi
Ramaria subbotrytis (Coker) Corner EMEdibleCoral fungi
Ramariopsis kunzei (Fr.) Corner EMEdibleCoral fungi
Resupinatus applicatus (Batsch) Gray WSOthersAgarics
Rhizocybe vermicularis (Fr.) Vizzini, P. Alvarado, G. Moreno, and Consiglio SSOthersAgarics
Rhizomarasmius undatus (Berk.) R.H. Petersen SSOthersAgarics
Rhodocollybia butyracea (Bull.) Lennox SSEdibleAgarics
Rhodocollybia prolixa (Fr.) Antonín and Noordel. SSOthersAgarics
Rickenella fibula (Bull.) Raithelh. EMOthersCantharelloid fungi
Ripartites tricholoma (Alb. and Schwein.) P. Karst. LSOthersAgaricsON683428
Russula adusta (Pers.) Fr. EMEdible, MedicinalAgarics
Russula aeruginea Lindblad ex Fr. EMEdibleAgarics
Russula albida A. Blytt EMEdibleAgarics
Russula alutacea (Fr.) Fr. EMEdible, Medicinal, PoisonousAgarics
Russula amoena Quél. EMOthersAgarics
Russula aurata Fr. EMOthersAgarics
Russula aurea Pers. EMOthersAgarics
Russula chloroides (Krombh.) Bres. EMEdibleAgarics
Russula crustosa Peck EMEdible, MedicinalAgaricsON683429
Russula cyanoxantha (Schaeff.) Fr. EMEdible, MedicinalAgaricsON683430
Russula delica Fr. EMEdible, MedicinalAgarics
Russula densifolia Secr. ex Gillet EMEdible, MedicinalAgaricsON683487
Russula emetica (Schaeff.) Pers. EMEdible, Medicinal, PoisonousAgarics
Russula exalbicans (Pers.) Melzer and Zvára EMEdibleAgarics
Russula faginea Romagn. EMEdibleAgarics
Russula flavida Frost ex Peck EMPoisonousAgarics
Russula foetens Pers. EMMedicinal, PoisonousAgaricsON683488
Russula fragilis Fr. EMMedicinal, PoisonousAgaricsON683489
Russula furcata Pers. EMEdibleAgarics
Russula grata Britzelm. EMOthersAgarics
Russula integra (L.) Fr. EMEdible, MedicinalAgarics
Russula lilacea Quél. EMEdible, MedicinalAgarics
Russula mariae Peck EMEdibleAgarics
Russula mustelina Fr. EMEdibleAgarics
Russula nauseosa (Pers.) Fr. EMEdibleAgarics
Russula paludosa Britzelm. EMEdibleAgarics
Russula pectinata Fr. EMPoisonousAgarics
Russula pseudodelica J.E. Lange EMEdible, MedicinalAgarics
Russula puellaris Fr. EMEdibleAgarics
Russula pungens Beardslee EMOthersAgarics
Russula risigallina (Batsch) Sacc. EMEdibleAgarics
Russula rosea Pers. EMEdible, MedicinalAgarics
Russula rubra (Lam.) Fr. EMEdibleAgarics
Russula sanguinaria (Schumach.) Rauschert EMEdibleAgarics
Russula sanguinea Fr. EMOthersAgarics
Russula sororia (Fr.) Romell EMMedicinalAgaricsON683431
Russula squalida Peck EMOthersAgarics
Russula subdepallens Peck EMEdibleAgarics
Russula vinosa Lindblad EMOthersAgaricsON683432
Sarcodontia spumea (Sowerby) Spirin EMOthersPHT fungi
Sarcomyxa edulis (Y.C. Dai, Niemelä, and G.F. Qin) T. Saito, Tonouchi, and T. Harada WSMedicinalAgarics
Sarcoscypha coccinea (Gray) Boud. WSPoisonousLarger Ascomycetes
Schizophyllum commune Fr.WSEdible, MedicinalAgarics
Scleroderma areolatum Ehrenb. SSEdible, Medicinal, PoisonousGasteroid fungi
Scleroderma bovista Fr. SSEdible, MedicinalGasteroid fungi
Scleroderma polyrhizum (J.F. Gmel.) Pers. SSEdible, MedicinalGasteroid fungi
Scutellinia pseudovitreola W.Y. Zhuang and Zhu L. Yang WSOthersLarger Ascomycetes
Scutellinia scutellata (L.) Lambotte WSOthersLarger Ascomycetes
Sparassis latifolia Y.C. Dai and Zheng Wang WSEdible, MedicinalPHT fungiON683490
Spathularia flavida Pers. SSOthersLarger Ascomycetes
Sphaerobolus stellatus Tode WSOthersGasteroid fungi
Spongiporus zebra (Y.L. Wei and W.M. Qin) B.K. Cui, L.L. Shen, and Y.C. Dai WSOthersPHT fungi
Steccherinum ochraceum (Pers. ex J.F. Gmel.) Gray WSOthersPHT fungi
Steccherinum rawakense (Pers.) Banker WSOthersPHT fungi
Stereum hirsutum (Willd.) Pers. WSMedicinalPHT fungi
Stereum rugosum Pers. WSOthersPHT fungi
Stereum subtomentosum Pouzar WSOthersPHT fungi
Stereum ostrea (Blume and T. Nees) Fr. WSOthersPHT fungi
Strobilurus stephanocystis (Kühner and Romagn. ex Hora) Singer WSOthersAgarics
Stropharia aeruginosa (Curtis) Quél. SSEdible, PoisonousAgarics
Stropharia rugosoannulata Farl. ex Murrill SSEdible, MedicinalAgarics
Suillellus luridus (Schaeff.) Murrill EMEdible, MedicinalBoletes
Suillus bovinus (L.) Roussel EMEdible, Medicinal, PoisonousBoletes
Suillus flavus (Quél.) Singer EMOthersBoletes
Suillus granulatus (L.) Roussel EMEdible, Medicinal, PoisonousBoletesON683433
Suillus grevillei (Klotzsch) Singer EMEdible, MedicinalBoletes
Suillus lactifluus (With.) A.H. Sm. and Thiers EMEdibleBoletes
Suillus laricinus (Berk.) Kuntze EMOthersBoletes
Suillus luteus (L.) Roussel EMEdible, Medicinal, PoisonousBoletes
Suillus spraguei (Berk. and M.A. Curtis) Kuntze EMOthersBoletes
Suillus subaureus (Peck) Snell EMEdible, MedicinalBoletes
Suillus viscidus (L.) Roussel EMEdible, MedicinalBoletes
Tapinella atrotomentosa (Batsch) Šutara EMMedicinal, PoisonousBoletes
Tapinella panuoides (Fr.) E.-J. Gilbert EMPoisonousBoletes
Terana caerulea (Lam.) Kuntze WSOthersPHT fungi
Tetrapyrgos nigripes (Fr.) E. Horak WSOthersAgarics
Thelephora anthocephala (Bull.) Fr. SSOthersPHT fungi
Thelephora palmata (Scop.) Fr. SSOthersPHT fungi
Tolypocladium capitatum (Holmsk.) C.A. Quandt, Kepler, and Spatafora EIOthersLarger Ascomycetes
Trametes coccinea (Fr.) Hai J. Li and S.H. He WSOthersPHT fungi
Trametes conchifer (Schwein.) Pilát WSOthersPHT fungi
Trametes gibbosa (Pers.) Fr. WSMedicinalPHT fungiON683491
Trametes hirsuta (Wulfen) Lloyd WSMedicinalPHT fungi
Trametes membranacea (Sw.) Kreisel WSOthersPHT fungi
Trametes pubescens (Schumach.) Pilát WSEdible, Medicinal, PoisonousPHT fungi
Trametes suaveolens (L.) Fr. WSMedicinalPHT fungi
Trametes trogi Berk. WSPoisonousPHT fungi
Trametes versicolor (L.) Lloyd WSMedicinalPHT fungiON683492
Tremella aurantia Schwein. WSEdibleJelly fungi
Tremella foliacea Pers. WSOthersJelly fungiON683493
Tremella fuciformis Berk. WSEdible, MedicinalBoletes
Tremella mesenterica (Schaeff.) Pers. WSEdible, MedicinalJelly fungi
Trichaptum abietinum (Pers. ex J.F. Gmel.) Ryvarden WSMedicinalPHT fungi
Trichaptum biforme (Fr.) Ryvarden WSMedicinalPHT fungi
Trichaptum pargamenum (Fr.) G. Cunn. WSOthersPHT fungi
Tricholoma acerbum (Bull.) Quél. EMEdible, Medicinal, PoisonousAgarics
Tricholoma album (Schaeff.) P. Kumm. EMEdible, Medicinal, PoisonousAgarics
Tricholoma aurantium (Schaeff.) Ricken EMOthersAgarics
Tricholoma equestre (L.) P. Kumm. EMEdible, PoisonousAgarics
Tricholoma matsutake (S. Ito and S. Imai) Singer EMEdible, MedicinalAgarics
Tricholoma scalpturatum (Fr.) Quél. EMEdible, PoisonousAgarics
Tricholoma terreum (Schaeff.) P. Kumm. EMOthersAgarics
Tricholoma tigrinum (Schaeff.) Gillet EMPoisonousAgarics
Tricholoma vaccinum (Schaeff.) P. Kumm. EMEdible, MedicinalAgarics
Tricholomopsis decora (Fr.) Singer WSEdibleAgarics
Tricholomopsis rutilans (Schaeff.) SingerWSPoisonousAgarics
Tulostoma bonianum Pat. SSOthersGasteroid fungi
Turbinellus floccosus (Schwein.) Earle ex Giachini and Castellano EMPoisonousCantharelloid fungi
Verpa bohemica (Krombh.) J. Schröt. SSEdible, Medicinal, PoisonousLarger Ascomycetes
Verpa digitaliformis Pers. SSEdibleLarger Ascomycetes
Vitreoporus dichrous (Fr.) Zmitr. WSOthersPHT fungi
Volvariella bombycina (Schaeff.) Singer WSEdible, MedicinalAgarics
Volvariella pusilla (Pers.) Singer SSEdible, MedicinalAgarics
Volvopluteus gloiocephalus (DC.) Vizzini, Contu and Justo SSPoisonousAgarics
Xanthochrous gilvicolor (Lloyd) Teng WSOthersPHT fungi
Xerocomellus chrysenteron (Bull.) Šutara EMOthersBoletes
Xerocomus chrysenteron (Bull.) Quél. EMOthersBoletes
Xeromphalina campanella (Batsch) Kühner and Maire WSMedicinalAgarics
Xerula pudens (Pers.) Singer WSOthersAgarics
Xylaria carpophila (Pers.) Fr. WSMedicinalLarger Ascomycetes
Xylaria hypoxylon (L.) Grev. WSOthersLarger Ascomycetes
Xylaria polymorpha (Pers.) Grev. WSOthersLarger Ascomycetes
Note: EM = ectomycorrhizal; SS = soil saprotroph; WS = wood saprotroph; LS = litter saprotroph; DS = dung saprotroph; EI = endophyte insect pathogen.
Table A2. Species scientific names and their corresponding abbreviations.
Table A2. Species scientific names and their corresponding abbreviations.
AbbreviationGenusAbbreviationGenusAbbreviationGenusAbbreviationGenus
AboAbortiporusDacDacrymycesLecLeccinumPipPiptoporus
AgaAgaricusDacrDacryopinaxLenLentinellusPlePleurotus
AgrAgrocybeDaeDaedaleaLentLentinusPluPluteus
AleAleuriaDaedDaedaleopsisLenzLenzitesPolPolyporus
AmaAmanitaDalDaldiniaLeoLeotiaPolyPolystictus
AmpAmpulloclitocybeDecDeconicaLepLepiotaPosPostia
ApiApioperdonDesDescoleaLepiLepistaPsaPsathyrella
ArmArmillariaDumDumontiniaLeuLeucoagaricusPsePseudoclitocybe
ArtArtomycesEntEntolomaLeucLeucocybePseuPseudosperma
AscAscocoryneExiExidiaLycLycoperdonPtePterula
AurAuriculariaFlamFlammulasterLyoLyophyllumPycPycnoporus
AuriAuriscalpiumFlammFlammulinaLysLysurusRadRadulodon
BisBisporellaFomFomesMacMacrocystidiaRamRamaria
BjeBjerkanderaFomiFomitopsisMacrMacrolepiotaResResupinatus
Bol1BoletinellusGalGalerinaMarMarasmiellusRhoRhodocollybia
BolBoletusGanGanodermaMaraMarasmiusRicRickenella
Cal1CaloceraGeaGeastrumMelMelanoleucaRusRussula
CaloCalocybeGerGerronemaMorMorchellaSarSarcodontia
CalCalvatiaGloGloeophyllumMucMucidulaSarSarcomyxa
CanCantharellusGloeGloeostereumMutMutinusSarcSarcoscypha
CerCerioporusGueGuepiniaMycMycenaSchSchizophyllum
CheCheilymeniaGymGymnopilusNeoNeofavolusSclScleroderma
ChlChlorociboriaGymnGymnopusNeolNeolentinusScuScutellinia
ChrChroogomphusHarHarryaOmpOmphalotusSpaSpathularia
ClaClavariaHelHelvellaOphOphiocordycepsSteSteccherinum
ClavClavariadelphusHemHemistrophariaOssOssicaulisSteStereum
ClavuClavulinaHerHericiumOtiOtideaStrStropharia
ClavulClavulinopsisHetHeterobasidionPanPanaeolusSuiSuillus
CliClitocybeHohHohenbueheliaPanePanellusTapTapinella
ColColtriciaHumHumariaPanuPanusTerTerana
ConConnopusHydHydnumParParalepistaTheThelephora
ConoConocybeHygHygrocybeParaParasolaTraTrametes
CopCoprinellusHygrHygrophorusPaxPaxillusTreTremella
CoprCoprinopsisHymHymenopellisPerPerenniporiaTriTrichaptum
CopriCoprinusHypHypholomaPezPezizaTricTricholoma
CorCordycepsHypHypsizygusPhaPhaeolepiotaTrichTricholomopsis
CoriCoriolopsisInfInfundibulicybePhaePhaeotremellaTulTulostoma
CortCortinariusInoInocybePhaPhallusTurTurbinellus
CotCotylidiaInoInonotusPhePhellinusVolVolvariella
CreCrepidotusIrpIrpexPhelPhellodonVolvVolvopluteus
CupCuphophyllusKueKuehneromycesPhlPhloeomanaXer1Xerocomus
CyaCyathusLacLaccariaPhoPholiotaXerXeromphalina
CycCyclocybeLactLactariusPhyPhyllotopsisXylXylaria
CysCystodermaLaeLaetiporusPicPicipes

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Figure 1. Distribution map showing the investigation sites in Jilin Province (A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park).
Figure 1. Distribution map showing the investigation sites in Jilin Province (A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park).
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Figure 2. Forest types from the investigation sites in Jilin Province. (A) Betula platyphylla forest; (B) Cunninghamia forest; (C) broadleaf mixed forest (mainly Acer sp.); (DF) Pine forest; (G) Quercus mongolica forest; (H) Coniferous and broadleaf mixed forest (Pinus and broadleaf mixed forest); (I) Quercus mongolica forest.
Figure 2. Forest types from the investigation sites in Jilin Province. (A) Betula platyphylla forest; (B) Cunninghamia forest; (C) broadleaf mixed forest (mainly Acer sp.); (DF) Pine forest; (G) Quercus mongolica forest; (H) Coniferous and broadleaf mixed forest (Pinus and broadleaf mixed forest); (I) Quercus mongolica forest.
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Figure 3. An example of field record and microscopic observation record of the collected specimen.
Figure 3. An example of field record and microscopic observation record of the collected specimen.
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Figure 4. Circos plot shows the relative abundance of macrofungi in six different sites in Jinlin Province based on the genera with more than four species. The analysis of species abundance shows Russula was the common genus and site A1 contains more species than the other five investigation sites. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Form; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
Figure 4. Circos plot shows the relative abundance of macrofungi in six different sites in Jinlin Province based on the genera with more than four species. The analysis of species abundance shows Russula was the common genus and site A1 contains more species than the other five investigation sites. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Form; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
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Figure 5. The co-occurring genera and species were analyzed in six different investigation sites in Jilin Province. (A) Co-occurring genera analysis in six investigation sites; 23 genera co-occur in six investigation sites; site B2 has the fewest endemic genera and C2 has the most. (B) Co-occurring species analysis in six investigation sites; 11 species occur in all six investigation sites; site A1 has the most endemic species, while site B2 has the fewest. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
Figure 5. The co-occurring genera and species were analyzed in six different investigation sites in Jilin Province. (A) Co-occurring genera analysis in six investigation sites; 23 genera co-occur in six investigation sites; site B2 has the fewest endemic genera and C2 has the most. (B) Co-occurring species analysis in six investigation sites; 11 species occur in all six investigation sites; site A1 has the most endemic species, while site B2 has the fewest. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
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Figure 6. Distribution proportions for different types of macrofungi in six different investigation sites from Jilin Province. (A) Analysis of all recorded species composition types of our investigation sites; Agarics were the most common macrofungi while Canthralloid fungi were rare. (B) Species composition type analysis of every investigation site; Agarics were predominant at every site, Cantharelloid fungi were rare at all sites, and the compositions of macrofungi at six investigation sites were enormously different. PHT fungi: Polyporoid, Hyonaceous and Thelephoroid fungi; A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
Figure 6. Distribution proportions for different types of macrofungi in six different investigation sites from Jilin Province. (A) Analysis of all recorded species composition types of our investigation sites; Agarics were the most common macrofungi while Canthralloid fungi were rare. (B) Species composition type analysis of every investigation site; Agarics were predominant at every site, Cantharelloid fungi were rare at all sites, and the compositions of macrofungi at six investigation sites were enormously different. PHT fungi: Polyporoid, Hyonaceous and Thelephoroid fungi; A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
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Figure 7. Diversity index analysis at genus level in six different investigation sites from Jilin Province. (A) Simpson diversity analysis in six different investigation sites from Jilin Province; the Simpson diversity index revealed site B2 was higher than the other five sites. (B) Shannon–Wiener diversity analysis in six different investigation sites from Jilin Province; the Shannon–Wiener diversity analysis showed site B2 was higher than the other five investigation sites. This result indicated that site B2 had the richest species diversity at the genus level and the most uniform distribution of species quantity. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
Figure 7. Diversity index analysis at genus level in six different investigation sites from Jilin Province. (A) Simpson diversity analysis in six different investigation sites from Jilin Province; the Simpson diversity index revealed site B2 was higher than the other five sites. (B) Shannon–Wiener diversity analysis in six different investigation sites from Jilin Province; the Shannon–Wiener diversity analysis showed site B2 was higher than the other five investigation sites. This result indicated that site B2 had the richest species diversity at the genus level and the most uniform distribution of species quantity. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
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Figure 8. Dominant families and genera of six investigation sites from Jilin Province. (A) Dominant families (number of species more than ten of the family) analysis of six investigation sites from Jilin Province. (B) Dominant genera (number of species more than five of the genera) analysis of six investigation sites from Jilin Province. The results show site A1 contains more dominant families and genera in six investigation sites; in contrast, site B2 includes few. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
Figure 8. Dominant families and genera of six investigation sites from Jilin Province. (A) Dominant families (number of species more than ten of the family) analysis of six investigation sites from Jilin Province. (B) Dominant genera (number of species more than five of the genera) analysis of six investigation sites from Jilin Province. The results show site A1 contains more dominant families and genera in six investigation sites; in contrast, site B2 includes few. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
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Figure 9. Relationship between macrofungi occurrence and month in three different investigation sites from Jilin Province. The results showed that they mostly arose from July to September. A1: Quanshuidong Forest Farm; B1: Shengli River Forest Farm; C2: Jingyuetan National Forest Park.
Figure 9. Relationship between macrofungi occurrence and month in three different investigation sites from Jilin Province. The results showed that they mostly arose from July to September. A1: Quanshuidong Forest Farm; B1: Shengli River Forest Farm; C2: Jingyuetan National Forest Park.
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Figure 10. Effect of air humidity on the occurrence of macrofungi in three different investigation sites from Jilin Province. (A) Quanshuidong Forest Farm; (B) Shengli River Forest Farm; (C) Jingyuetan National Forest Park.
Figure 10. Effect of air humidity on the occurrence of macrofungi in three different investigation sites from Jilin Province. (A) Quanshuidong Forest Farm; (B) Shengli River Forest Farm; (C) Jingyuetan National Forest Park.
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Figure 11. Effect of precipitation on the occurrence of macrofungi in three different investigation sites from Jilin Province. (A) Quanshuidong Forest Farm; (B) Shengli River Forest Farm; (C) Jingyuetan National Forest Park.
Figure 11. Effect of precipitation on the occurrence of macrofungi in three different investigation sites from Jilin Province. (A) Quanshuidong Forest Farm; (B) Shengli River Forest Farm; (C) Jingyuetan National Forest Park.
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Figure 12. Effect of temperature on the occurrence of macrofungi in three different investigation sites from Jilin Province. (A) Quanshuidong Forest Farm; (B) Shengli River Forest Farm; (C) Jingyuetan National Forest Park.
Figure 12. Effect of temperature on the occurrence of macrofungi in three different investigation sites from Jilin Province. (A) Quanshuidong Forest Farm; (B) Shengli River Forest Farm; (C) Jingyuetan National Forest Park.
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Figure 13. Canonical correspondence analysis (CCA) of the selected environmental factors and the recorded macrofungi species. All displayed environmental factors passed the most significant test (p < 0.05); P: mean precipitation from July to September; S: mean wind speed from July to September; RH: mean humidity from July to September; A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park. Letters are composed of the first three- or four-letter abbreviations of the scientific name, and the corresponding words are provided in Table A2.
Figure 13. Canonical correspondence analysis (CCA) of the selected environmental factors and the recorded macrofungi species. All displayed environmental factors passed the most significant test (p < 0.05); P: mean precipitation from July to September; S: mean wind speed from July to September; RH: mean humidity from July to September; A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park. Letters are composed of the first three- or four-letter abbreviations of the scientific name, and the corresponding words are provided in Table A2.
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Figure 14. Complex heatmap of the macrofungi composition (genus level) at six investigation sites from Jilin Province. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
Figure 14. Complex heatmap of the macrofungi composition (genus level) at six investigation sites from Jilin Province. A1: Quanshuidong Forest Farm; A2: Lushuihe National Forest Park; B1: Shengli River Forest Farm; B2: Longwan National Forest Park; C1: Zuojia Region; C2: Jingyuetan National Forest Park.
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Table 1. Geographical coordinates and vegetation of the investigation sites.
Table 1. Geographical coordinates and vegetation of the investigation sites.
Investigation SitesLongitudeLatitudeVegetationSoil TypeInvestigation Time
Quanshuidong Forest Farm (A1)128.89° E42.68° NPinus and broadleaf mixed forest, Quercus and Poplar forest, coniferous forests (Pinus koraiensis), Taxus cuspidata, Salix spp., etc.Dark brunisolic soil and planosol soil2014–2016
Lushuihe National Forest Park (A2)128.01° E42.55° N2013–2015
Mt. Laoyeling (Shengli River Forest Farm, B1)127.83° E43.69° NPinus koraiensis and broadleaf mixed forest, larch forest, Quercus mongolica forest, Acer truncatum, Tilia amurensis, and Fraxinus mandshurica, etc.Dark brunisolic soil and planosol soil2005–2007
Mt. Longgang (Longwan National Forest Park, B2)126.45° E42.37° NQuercus mongolica forest and broadleaf mixed forestDark brunisolic soil2011–2013
Zuojia Region (C1)126.16° E44.03° NQuercus mongolica forest, spruce forest, and pine forestBlack soil and paddy soil2011–2013
Jingyuetan national forest park (C2)125.48° E43.79° NLarch forest, Pinus forest, and Quercus mongolica forestDark brunisolic soil2003–2006
Table 2. Meteorological conditions and types of soil at the investigation sites.
Table 2. Meteorological conditions and types of soil at the investigation sites.
Investigation SiteThe Average Temperature from July to September/°C (T)The Average Relative Humidity from July to September/% (RH)The Average Monthly Precipitation from July to September/mm (P)The Average Wind Speed from July to September/m/s (S)The Accumulated Temperature from July to September/°C (AT)
Quanshuidong Forest Farm (A1)18.6080.67152.271.571715.90
Lushuihe Town (A2)19.6081.67143.271.671698.9
Mt. Laoyeling—Shengli River Forest Farm (B1)17.6779.00118.631.901629.80
Mt. Longgang—Longwan National Forest Park (B2)19.5378.33170.771.231746.40
Zuojia Region (C1)19.9377.00124.432.031838.60
Jingyuetan National Forest Park (C2)20.4374.00116.032.831884.30
Table 3. Mycorrhizal:saprophytic macrofungi ratios of the investigation sites from Jilin Province.
Table 3. Mycorrhizal:saprophytic macrofungi ratios of the investigation sites from Jilin Province.
SitesA1A2B1B2C1C2
Mycorrhizal927677306057
Saprophytic19717018175196175
Ratio/%0.470.450.430.400.310.33
Table 4. Top 10 families and genera in six different investigation sites from Jilin Province.
Table 4. Top 10 families and genera in six different investigation sites from Jilin Province.
No.FamilyNumbers of SpeciesPercentageGenusNumbers of SpeciesPercentage
1Agaricaceae527.07%Lactarius202.72%
2Polyporaceae506.80%Mycena192.59%
3Tricholomataceae415.58%Cortinarius182.45%
4Inocybaceae344.63%Marasmius182.45%
5Strophariaceae334.49%Pholiota182.45%
6Hygrophoraceae253.40%Agaricus162.18%
7Marasmiaceae253.40%Entoloma162.18%
8Mycenaceae233.13%Amanita141.90%
9Cortinariaceae192.59%Crepidotus131.77%
10Omphalotaceae182.45%Inocybe131.77%
Table 5. Similarity comparison between Mt. Changbai, its branches, and five other investigation sites.
Table 5. Similarity comparison between Mt. Changbai, its branches, and five other investigation sites.
LocationBCB1B2C1C2
S/%42.0639.9537.2332.3926.8530.88
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Hu, J.-J.; Zhao, G.-P.; Tuo, Y.-L.; Qi, Z.-X.; Yue, L.; Zhang, B.; Li, Y. Ecological Factors Influencing the Occurrence of Macrofungi from Eastern Mountainous Areas to the Central Plains of Jilin Province, China. J. Fungi 2022, 8, 871. https://doi.org/10.3390/jof8080871

AMA Style

Hu J-J, Zhao G-P, Tuo Y-L, Qi Z-X, Yue L, Zhang B, Li Y. Ecological Factors Influencing the Occurrence of Macrofungi from Eastern Mountainous Areas to the Central Plains of Jilin Province, China. Journal of Fungi. 2022; 8(8):871. https://doi.org/10.3390/jof8080871

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Hu, Jia-Jun, Gui-Ping Zhao, Yong-Lan Tuo, Zheng-Xiang Qi, Lei Yue, Bo Zhang, and Yu Li. 2022. "Ecological Factors Influencing the Occurrence of Macrofungi from Eastern Mountainous Areas to the Central Plains of Jilin Province, China" Journal of Fungi 8, no. 8: 871. https://doi.org/10.3390/jof8080871

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