ChapterPDF Available

Diversity and distribution of macrofungi in Kodagu region (Western Ghats) - A preliminary account.

Authors:

Abstract and Figures

This chapter provides preliminary observations on the diversity, distribution and ecology of macrofungi in selected biomes (sacred groves, reserve forests and agroforests) of Kodagu region of the Western Ghats. One-time survey of three biomes during monsoon season (August-October, 2011) yielded 25 species with a highest of 23 species in agroforests and the rest two biomes possess 12 species each. A brief description based on the field and laboratory studies along with substrates and distribution in the Western Ghats are given. None of the macrofungi was frequent in all biomes and nine species were restricted to agroforest sand one species each confined to sacred groves and reserve forests. Among the macrofungi recovered, a maximum of 17 species are known from the Western Ghats of Kerala followed by four species from Karnataka and one species from Tamil Nadu. Eight species were edible, five species were medicinal and one species was ectomycorrhizal, and all except for Tricholoma sp. were recovered from agroforests shows the potential of this biome of Kodagu region in cultivation and harnessing economically valuable macrofungi. Strategies and necessity of further exploration of macrofungi in different ecological niches of the Western Ghats are highlighted.
Content may be subject to copyright.
73
Chapter 2
_________________________________
Diversity and Distribution of
Macrofungi in Kodagu Region (Western
Ghats) A Preliminary Account
_________________________________
N.C. Karun1, K.R. Sridhar1* and K.A. Anu Appaiah2
1Department of Biosciences, Mangalore University, Mangalagangotri,
Mangalore 574 199, Karnataka, India
2Department of Food Microbiology, Central Food Technological
Institute, Mysore 570 020, Karnataka, India
(*Correspondence: E-mail: kandikere@gmail.com)
Karun, N.C., Sridhar, K.R. and Anu Appaiah, K.A. 2014. Diversity and
distribution of macrofungi in Kodagu region (Western Ghats) - A
preliminary account. Biodiversity in India, Volume 7 (Ed. Pullaiah, T.,
Karuppusamy, S. and Rani, S.). Regency Publications, New Delhi,
7396.
ABSTRACT
This chapter provides preliminary observations on the diversity,
distribution and ecology of macrofungi in selected biomes (sacred
groves, reserve forests and agroforests) of Kodagu region of the Western
Ghats. One-time survey of three biomes during monsoon season
(August-October, 2011) yielded 25 species with a highest of 23 species
in agroforests and the rest two biomes possess 12 species each. A brief
description based on the field and laboratory studies along with
substrates and distribution in the Western Ghats are given. None of the
macrofungi was frequent in all biomes and nine species were restricted
to agroforest sand one species each confined to sacred groves and
reserve forests. Among the macrofungi recovered, a maximum of 17
species are known from the Western Ghats of Kerala followed by four
74
species from Karnataka and one species from Tamil Nadu. Eight species
were edible, five species were medicinal and one species was
ectomycorrhizal, and all except for Tricholoma sp. were recovered from
agroforests shows the potential of this biome of Kodagu region in
cultivation and harnessing economically valuable macrofungi. Strategies
and necessity of further exploration of macrofungi in different ecological
niches of the Western Ghats are highlighted.
Keywords: Macrofungi, Mushrooms, Woodrot fungi, Western Ghats,
Sacred groves, Reserve forests, Agroforests, Plantations,
Diversity, Economic value
Introduction
Fungi constitute the third essential functional component after
flora and fauna as decomposers, symbionts and pathogens representing
highest global diversity between 1.5 and3 million species based on
continuous rise of reports on new species and in turn fungus/plant ratios
in tropics (Hawksworth, 2001, 2012). Macrofungi especially mushrooms
represent up to 41,000 species, of which about 850 species are recorded
from different parts of India especially in Himalayan and Western Ghat
region (Manoharachary et al., 2006). Like Himalayas, the Western Ghats
of India is also one of the most valuable natural repositories of macro-
and microfungi of the world. It runs 1,600 km (~160,000 km2) through
the western part of Deccan Plateau in Gujarat, Maharashtra, Goa,
Karnataka, Tamil Nadu and Kerala states passing through complex
reverine system encompassing a wide range of hills and mountains (up
to 1,200 m asl).
Some studies are available on the macrofungi in different parts of
the Western Ghats. Thomas et al. (2001) have reported 13 species
belonging to Bolbitiaceae from Kerala. In 25 sacred groves, 23 coffee
agroforests and 10 reserve forest sites in Karnataka, a total of 163
macrofungi were recovered and identified only up to genus level
(Bhagwath et al., 2005; Brown et al., 2006). Nearly 195 species and 28
species of agarics have been reported from the Nilgiri Biosphere
Reserve of Tamil Nadu and Kerala region (Natarajan et al., 2005a). Up
to 25 species of ectomycorrhizal fungi in dipterocarp evergreen
Kadamakkal Reserve Forest of Kodagu (Karnataka State) were
documented by Natarajan et al. (2005b). Twenty-five species of
Hygrocybe were described from Kerala by Leelavathy et al. (2006).
Riviere et al. (2007) compared the diversity of ectomycorrhizal fungi of
the rain forests of Africa and Western Ghats of India based
mitochondrial large subunit rRNA. Surveys in semi-evergreen and
moist-deciduous forests of Karnataka yielded 778 species of macrofungi
(Swapna et al., 2008). Twenty-two species of Lepiota, nine species of
Leucoagaricus and 15 species of Leucocoprinus were recorded from
Kerala (Kumar and Manimohan, 2009a, 2009b). Mohanan (2011)
documented 550 species (belonging to 51 families) from various parts of
Kerala. Ranadive et al. (2011) gave a checklist of 256 species of
Aphyllophorales from Maharashtra. A total of 68 species of mushrooms
were recovered from Thiribhuvanamala et al. (2011) from Tamil Nadu
and Kerala. Survey of Tamil Nadu and Karnataka yielded 56 species of
woodrot fungi (Selvam et al., 2012). However, compared to the diversity
75
of flora and fauna and varied ecological niches exists in the vast area of
Western Ghats, our knowledge on the macrofungal diversity,
distribution and ecological functions is limited. In this report,
occurrence, diversity and distribution of macrofungi from four protected
biomes (two each of sacred groves and reserve forests) and two
cultivated landscapes (coffee agroforests) of Kodagu region of the
Western Ghats based on one-time survey are reported with a brief
description of each species along with distribution in different parts of
the Western Ghats.
Study area and sampling
Kodagu District (formerly known as Coorg) in Karnataka State is
situated between 11°56', 12°52' N and 75°22', 76°11' E (Pascal and
Meher-Homji 1986). The mean temperature during the coldest months
(December-January) in the study area selected ranges between 8°C and
20°C, approximate rainfall ranges from 200-500 cm/annum and dry
season persists for about 3-4 months (February-May; 28-32°C). The
landscape of Kodagu consists of a large number of sacred groves,
reserve forests, tree-covered plantations and treeless cultivated lands
(Bhagwath et al., 2005). For example, sacred groves (known as
‘Devarakadu’) are common in Kodagu region occupied about 2% of the
landscape accounting one grove for every 300 ha, which vary in area
from a fraction of hectare up to a few tens of hectares (Kushalappa and
Bhagwat 2001; Bhagwath et al., 2005; Brown et al., 2006). The reserve
forests occupied up to 30% of the area, while the shade-grown
plantations occupied about 60% (e.g. coffee) and the treeless cultivated
lands occupied 8% (e.g. paddy).
Macrofungi were assessed in three biomes: i) Sacred groves
(Maggula and Bettoli); ii) Reserve forests (Sampaje and Makutta); iii)
Coffee agroforests (V’Badaga and B’Shettigeri) (Fig. 1). Sacred groves
studied have least human interference and encompass economically
valuable plant species those were maintained traditionally by the local
communities as a measure of biodiversity preservation and restoration
[Artocarpus hirsutus (wild jack), Canarium strictum (black dhupa),
Caryota urens (toddy palm), Dysoxylum malabaricum (white cedar),
Holigarna beddomei (kadu geru), H. nigra (kadu geru), Lagerstroemia
microcarpa (nandi), Mangifera indica (kadu mavu), Syzygium cuminii
(nerale), Toona ciliata (red cedar), and Vateria indica (white dhupa)].
Usually edible mushrooms like Lentinus and Pleurotus are common in
standing dead, woody litters and logs of C. strictum, D. malabaricum,
M. indica and V. indica. The reserve forests studied are located in hilly
zones with homogenous evergreen tree vegetation with high rainfall.
The agroforests studied consists of shade-grown coffee plantations with
common native (Artocarpus hirsutus, Dalbergia latifolia, Syzygium
cuminii and Toona ciliata) and exotic (Acacia mangium, Acrocarpous
fraxinifolius, Erythrina subumbrans and Grevelia robusta) tree species.
Opportunistic mode of sampling was performed in three biomes
during August (sacred groves), September (reserve forests) and October
(agroforests) 2011. In each sampling, an area of 50 m2 was intensely
surveyed for the presence of fruit bodies of woodrots and mushrooms.
Representative fruit bodies were sampled from different substrates like
soil, leaf/bark/twig/woody litter, rotting logs/stubs, termite mounds and
76
Figure 2.1. Map of the study area and biomes studied in Kodagu
District of Karnataka State of the Western Ghats.
Sacred grove: 1. Maggula, 2. Bettoli; Forest reserve: 3. Sampaje, 4.
Makutta; Agroforest: 5. V’Badaga, 6. B’Shettigeri.
standing dead trees. The snaps of each mushroom was taken on the spot,
fruit bodies were assessed for general features like type, colour,
dimension, extent of fruit bodies (solitary or gregarious) and substrates.
Part of fragile mushrooms possessing spores was fixed in lactophenol or
aniline-blue-lactophenol in labeled vials. Sturdy fruit bodies of
mushrooms were collected in labeled polythene bags and brought to the
laboratory for further observations. Spores of each mushroom were
evaluated based on the light microscopic observations. Each mushroom
was fixed (formalin-ethanol-water) and deposited in the herbarium of the
Department of Biosciences, Mangalore University(#
MUBSNCKKRSMF-002-026) (Fig. 2-5).A brief morphological
description of each fungus is given after confirming the identity based
on the monographs (Kibby, 1979; Purkayastha and Chandra, 1985;
Jordan, 1995; Mohanan, 2011) along with their substrates and
distribution.
Diversity and distribution
One-time survey in sacred groves, reserve forests and agroforests
in Kodagu region yielded 25 macrofungi (Table 1; Fig. 2.2-2.5).
Agroforests consists of a maximum of 23 species and the rest (sacred
groves and reserve forests) possess 12 species each. Eight species were
seen in all biomes (Auricularia auricula-judae, Cookeina tricholoma,
Daldinia concentrica, Ganoderma applanatum, Lentinus
dicholamellatus, Lenzites vespacea, Termitomyces tylerianus and
Xylaria longipes), nine species were restricted to agroforests
(Auricularia mescenterica, Clitocybe infundibuliformis, Crepitotus
variabilis,Exidia glandulosa, Gymnopilus junonius, Lentinus patulus,
77
Pleurotus pulmonarius, Ramaria sp. and Trogia infundibuliformis) and
one species each confined to the sacred groves (Polyporus sp.) and
reserve forests (Tricholoma sp.).None of the macrofungi was frequent in
all biomes. Only Cookeina tricholoma was frequent in sacred groves as
well as reserve forests, while A. auricula-judae, C. variabilis, C.
striatus, L. patulus and T. tylerianus were frequent in agroforests. Based
on published records, a maximum of 17 species are known from the
Western Ghats of Kerala followed by four species in Karnataka and one
species in Tamil Nadu. One species each of Geastrum, Ployporus,
Ramaria and Tricholomawas not identifiable up to species level and
seem to be new species to the Western Ghats needs further enquiry.
Among the macrofungi recorded, eight species were edible, fivespecies
were medicinal and one species was ectomycorrhizal based on literature
Table 1. Distribution of macrofungi in three biomes of Kodagu
region of the Western Ghats.
Species (Figure 2.2-2.5)
Sacred-
groves
Reserve
forests
Agro-
forests
Economic
value
Auricularia auricula-judae (Bull.) Quél. (2.2a)
++
++
+++
Edible and
medicinal
A. mescenterica (Dicks.) Pers. (2.2b & c)
-
-
++
Clitocybe infundibuliformis Quél. (2.2d & e)
-
-
+
Edible
Cookeina tricholoma (Mont.) Kuntze (2.2h)
+++
+++
+
Crepidotus variabilis (Pers.) P. Kumm. (2.2f & g)
-
-
+++
Cyathus striatus (Huds.) Willd. (2.2i)
+
-
+++
Daldinia concentrica (Bolton) Ces. & De Not. (3.3a)
++
++
++
Medicinal
Dictyophora cinnabarina W.S. Lee (2.2j)
-
+
+
Exidia glandulosa (Bull.) Fr. (3.3b)
-
-
+
Ganoderma applanatum (Pers.) Pat. (3.3c &d)
++
++
++
Medicinal
Geastrum sp. (3.3g)
+
-
++
Gymnopilus junonius (Fr.) P.D. Orton (3.3e & f)
-
-
+
Edible
Ileodictyon gracile Berk. (3.3h)
-
++
++
Lentinus dicholamellatus Manim. (4.4a & b)
+
+
++
Edible
L. patulus Lév. (4.4e)
-
-
+++
Lenzites vespacea (Pers.) Pat. (4.4c & d)
++
++
++
Panus conchatus (Bull.) Fr. (4.4g & h)
-
++
++
Pleurotus pulmonarius (Fr.) Quél. (4.4a & b)
-
-
++
Edible
Polyporus sp. (4.4c & d)
+
-
-
Ramaria sp. (4.4f)
-
-
++
Scleroderma verrucosum (Bull.) Pers. (5.5e)
++
-
++
Edible and
Ectomycorrhizal
Termitomyces tylerianus Otieno (5.5f & g)
++
++
+++
Edible and
medicinal
Tricholoma sp. (5.5i & j)
-
++
-
Edible
Trogia infundibuliformis Berk. & Broome (5.5h)
-
-
++
Xylaria longipes Nitschke (5.5k)
++
++
++
Medicinal
Total species
12
12
23
-, not found; +, rare; ++, common; +++, frequent
and traditional knowledge (Purkayastha and Chandra, 1985; Jordan,
1995; Puttaraju et al, 2006; Das, 2010; Jha et al., 2011; Mohanan, 2011).
All of them (except for Tricholoma sp.) were recovered from the
78
agroforests shows the potential of this biome in Kodagu region for
cultivation and harnessing economically important macrofungi.
Description
Auricularia auricula-judae (Bull.) Quél. (Fig. 2.2a) (Auriculariaceae
Basidimycotina) (# MUBSNCKKRSMF-002)
Non-gilled, small to medium, fleshy, neither encrusting nor
bracket-like, purple brown to grey brown, fruit bodies sessile, ear-like,
grow in clusters, annual, lignicolous, odour and taste not distinctive,
edible and medicinal.
Fruit body. Upper surface purple brown with grey tinge when
damp, shiny, lower surface grey brown, shiny, smooth becoming
wrinkled, inverted cup-/irregular bracket (flabelliform)/fan-shaped, often
fused with adjacent fruit bodies and narrowly attached: 4.4 (2.1-6.2) cm
diam. (n=10). Flesh purple brown, gelatinous, tough and rubbery when
damp, and hard and brittle on drying.
Spores. Hyaline, allantoid or cylindrical and smooth: 12.9 (11.1-
13.9) ×5.2 (4.7-5.5) µm (n=10).
Substrate. Rotting logs and bark of Acacia mangium, Acrocarpus
fraxinifolius, Artocarpus hirsutus, Careya arborea, Olea dioica and
Toona ciliata.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Karnataka (Swapna et al., 2008), Tamil Nadu
(Johnsy et al., 2011; Sargunum et al., 2012) and Kerala (Mohanan,
2011).
Auricularia mesentrica (Bull.) Quél. (Fig. 2.2b and c) (Auriculariaceae
Basidimycotina) (# MUBSNCKKRSMF-003)
Non-gilled, small to medium, fleshy, neither encrusting nor
bracket-like, purple brown to grey brown, fruit bodies sessile, ear-like,
grow in tires, annual, lignicolous, infrequent, odour and taste are not
distinctive and inedible.
Fruit body. Upper surface brownish-grey, zoned, more pallid at
margin, hairy, lobed margin, initially disc-shaped and becoming
expanded into densely tiered brackets. Under surface reddish purple,
wrinkled, white and pruinose: 3.5 (1.1-4.8) cm diam. (n=14). Flesh
brown, gelatinous, elastic when damp, hard and brittle when dry.
Spores. Hyaline, smooth and ellipsoidal: 8.5 (6.6-9.7) × 5.4 (4.6-
5.9) µm (n=10).
Substrate. Rotting logs and bark of Memecylon umbellatum and
Syzygium cumini.
Occurrence. Coffee agroforest in B’Shettigeri.
Distribution. Kerala (Mohanan, 2011).
Clitocybe infundibuliformis Quél. (Fig. 2.2d and e) (Tricholomataceae
Basidiomycotina) (# MUBSNCKKRSMF-004)
Gilled, medium-size agaric, fleshy, stipe central, foamy white,
solitary or in small troops, annual, rare, humicolous/lignicolous, odour
of almonds, taste not distinctive and edible.
Cap. Whitish to cream, smooth and silky, infundibuliform with
typical wavy margin: 1.8-6.6 cm (n=5). Flesh whitish, thick and soft.
79
Gills. Creamish, deeply decurrent, narrow and crowded.
Spore. Hyaline, smooth and ellipsoidal: 5.9 (4-7.9) × 3.2 (2.6-4)
µm (n=14).
Stipe. Concolorous with cap, smooth, equal and slightly swollen
at base: 0.7-1.8 cm tall × 0.2-0.4 cm thick (n=5). Flesh creamish,
tougher than in cap and partly stuffed or hollow.
Substrate. On the decomposing coir of Cocos nucifera.
Occurrence. Coffee agroforest in V’Badaga.
Distribution. Not known.
Cookeina tricholoma(Mont.) Kuntze (Fig. 2.2h) (Sarcocyphaceae
Ascomycotina) (# MUBSNCKKRSMF-005)
Small to medium, top shaped, fleshy, orange, spiny, in trooping
groups/clusters, frequent, annual, lignicolous, odour and taste not
distinctive and inedible.
Fruit body. Orange coloured, fading to pinkish-orange with age,
deeply cup- to funnel-shaped: 2.1 (1.3- 2.4) × 2.8 (2.2-3.6) cm (n=10),
sparse long whitish hairs throughout, more hairs towards margin,
without hairs on stipe, inner hymenial surface orange coloured, smooth
and bears sporangium.
Asci. Cylindrical and equal: 320.9 (289.3-341.9) × 19.9 (18.4-21)
µm.
Spores. Hyaline, smooth and broadly fusiform: 28.9 (26.8-31.6)
× 14.1 (11.8-16.3) µm.
Stipe. Smooth, equal and hallow: 1.5 (0.4-2.8) × 0.4 (0.3-0.5) cm
(n=10).
Substrate. On rotting twigs of Canarium strictum, Dysoxylum
malabaricum, Euodia lunu-ankenda, Toona ciliate and Vateria indica.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Kerala (Mohanan, 2011).
Crepidotus variabilis(Pers.) P. Kumm. (Fig. 2.2f and g) (Crepidotaceae
Basidiomycotina) (# MUBSNCKKRSMF-006)
Gilled, small, fleshy, sessile, whitish to creamish, irregular, in
trooping groups/clusters, annual, rare, lignicolous, odour and taste not
distinctive and inedible.
Fruit body. Upper surface whitish become creamish with age,
kidney or reniform or irregularly fan-shaped or lobed and faintly striate
towards the margin: 1.7 (0.7-2) cm (n=9). Flesh white, thin, soft and
brittle.
Gills. Whitish becoming pink-violet, decurrent and fairly
crowded.
Spores. Pinkish-brown, minutely warty and elongated to
ellipsoidal: 7.5 (5.3-7.9) × 4.7 (3.3-5.3) µm(n=10).
Stipe. Lateral, rudimentary or absent.
Substrate. On the rotting burnt Bambusa sp. and rotting twigs of
Jatropha curcas.
Occurrence. Coffee agroforest in B’Shettigeri.
Distribution. Not known.
80
Cyathus striatus (Huds.) Willd. (Fig. 2.2i) (Nidulariaceae
Basidiomycotina) (# MUBSNCKKRSMF-007)
Non-gilled, small, cone-/trumpet-shaped, leathery, blackish-
greyish brown, hairy, in small clusters, rare, annual, lignicolous, odour
and taste not distinctive and inedible.
Fruit body. Cone- or trumpet-shape dperidium: 0.9 (0.8-0.9) ×
0.8 (0.7-0.9) cm (n=10). Outer surface brownish, shaggy and covered in
fine felty hairs. Inner surface greyish-brown to greyish-silver, vertically
striated and covered by operculum (whitish membrane), which ruptures
at maturity to expose several (20-30) greyish-white lens shaped ‘eggs’
(peridioles) (2mm diam.), immersed in mucilage at the base and attached
by fine mycelial strands. Flesh soft, paper-thin and resistant.
Spores. Hyaline, smooth and ellipsoidal: 6.8 (5.3-7.9) × 3.7 (2.9-
4) µm (n=10).
Substrate. On rotting twigs of Aporusa lindleyana, Euodia lunu-
ankenda, Erythrina subumbrans and on soil rich with woody debris.
Occurrence. Sacred grove in Bettoli and coffee agroforest in
B’Shettigeri.
Distribution. Karnataka (Swapna et al., 2008) and Kerala
(Mohanan, 2011).
Daldinia concentrica (Bolton) Ces. & De Not. (Fig. 2.3a) (Xylariaceae
Ascomycotina) (# MUBSNCKKRSMF-008)
Small to medium, irregularly sub-spherical, tough and woody,
reddish-brown to purple brown, sessile, annual, frequent, lignicolous,
solitary to gregarious, odour and taste not distinctive, inedible and
medicinal.
Fruit body. Stroma reddish-purple brown, becoming black with
age by shedding black spores, sub-spherical, sometimes shiny, ostiolate:
5.1 (1.8-7.8) cm diam. (n=12). Perithecia black, sub-spherical,
embedded in stromatal tissue in single layer below the surface. Flesh
blackish-grey with zebra-banded silver sheen on cut surface, hard, brittle
and fibrous.
Asci. Baseball bat-shaped, long and 8-spored: 141.5 (113.1-
173.6) × 9.2 (6.8-10.5) (n=10).
Spores. Black, smooth and ellipsoidal with longitudinal slit 12.5
(11.6-15.1) × 5.6 (5.3-6.1) (n=10).
Substrate. Rotting logs and bark of Acacia mangium, Acrocarpus
fraxinifolius, Artocarpus hirsutus, Careya arborea and Toona ciliata.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Karnataka (Swapna et al., 2008) and Kerala
(Mohanan, 2011).
Dictyophora cinnabarina W.S. Lee (Fig. 2.2j) (Phallaceae
Basidiomycotina) (# MUBSNCKKRSMF-009)
Non-gilled, medium, fleshy, phallic, white stipe with brownish
head and orange net, solitary, annual, rare, silvicolous, odour
foetid/stringent, taste not distinctive and inedible.
81
Figure 2.2. Photographs of macrofungi of Kadagu region.
a: Auricularia auricula-judae on wood; b and c: A. mescenterica on
wood; d and e: Clitocybe infundibuliformis on coconut surface (coir);
f and g: Crepidotus variabilis on wood; h: Cookeina tricholoma on
bark and wood; i: Cyathus striatus on twigs and embedded in soil;
j: Dictyophora cinnabarina on soil.
82
Figure 2.3. Photographs of macrofungi of Kadagu region.
a: Daldinia concentrica on wood; b: Exidia glandulosa on wood; c
and d: Ganoderma applanatum on wood; e and f: Gymnopilus
junonius on burnt soil; g: Geastrum sp. on leaves, twigs and soil; h:
Ileodictyon gracile on twigs.
83
Fruit body. White egg, sub-spherical, resistant to rubbery outer
membrane with gelatinous matrix separated from the embryonic spore
mass and stipe by an inner membrane. Attached to soil by a rhizomorphs
(3-4) and on maturity the egg ruptures and the spore mass are carried
rapidly upward on the receptacle in tip of stipe. Stipe whitish, honey-
combed, cylindrical, spongy, hollow: 13.1 (12.9-13.3)× 1.7 (1.6-1.7) cm
(n=3) and leaving membranous volva around the base of stipe. Volva
white to creamish or yellowish brown, thickly gelatinous, soft: 3.6 (3.5-
3.8)cm diam. (n=3), surmounted by a greyish yellow to brownish yellow
conical head carrying the spore mass and orange indusium hanging out
from under the lower margin. The head is strongly chambered, bears a
reticulate mesh of raised ribs with apical disc perforated in centre and
surrounded throughout with dark olive-green to metallic green
mucilaginous gleba (spore mass): 2.2 (2.1-2.3) × 2.2 (2-2.3) cm (n=3).
Indusium orange to yellowish orange, netted, partly elastic and flaring at
bottom: 6.9 (6.7-7.1) cm height (n=3).
Spores. Smooth, ellipsoidal and hyaline. 3.3 (2.6-3.9) × 1.3 (1.1-
1.6) µm (n=10).
Substrate. Soil below the trees of Lagerstroemia microcarpa.
Occurrence. Reserve forest in Sampaje and coffee agroforest in
V’Badaga.
Distribution. Karnataka (Abrar et al., 2007; Swapna et al., 2008)
and Kerala (Mohanan, 2011).
Exidia glandulosa (Bull.) Fr. (Fig. 2.3b) (Tremellaceae
Basidiomycotina) (# MUBSNCKKRSMF-010)
Non-gilled, small to medium, gelatinous, blackish brown to
blackish ash, sessile, contorted disc-shaped, grow in groups, annual,
lignicolous, rare, odour and taste not distinctive and inedible.
Fruit body. Brownish when damp, ash black when dry, expanses
of tissues appear like brain folding and fused with adjacent sporophores,
smooth, shiny with glandular warts and sessile. Under surface creamish,
wrinkled and wholly attached to the decaying log: 2.8 (1.6-4.7) cm diam.
(n=5). Flesh brownish gelatinous/soft when damp, dry on hard, become
thin and membranous.
Spores. Hyaline, smooth and ellipsoidal: 8.1 (6.6-9.2) × 4.7 (3.9-
5.3) µm (n=10).
Substrate. On the rotting logs of Artocarpus heterophyllus.
Occurrence. Coffee agroforest in B’Shettigeri.
Distribution. Not known.
Ganoderma applanatum (Pers.) Pat. (Fig. 2.3c and d)
(Ganodermataceae Basidiomycotina) (# MUBSNCKKRSMF-011)
Non-gilled, large to very large, woody bracket, sessile, grey-
brown, grow in limited overlapping tiers, perennial, lignicolous,
common on wood, odour fungoid, taste bitter, inedible and medicinal.
Fruit body. Greyish-brown, often discoloured into reddish brown
or cocoa brown from deposited spores, generally flattened, radially wavy
or wrinkled, concentrically grooved and zoned, broadly attached, sessile:
18.8 (12.6-24.9) cm diam. (n=5). Flesh dark brick, thicker than the tube
region, very tough and fibrous.
84
Pores. White, bruising brown and circular in annual layers.
Spores. Brown, warty, ovoid to broadly ellipsoidal and flattened
at one end with hyaline germ pore: 7.8 (7.7-7.9) × 5.4 (5.3-5.9) µm
(n=14).
Substrate. Rotting trunks of Artocarpus heterophyllus and A.
hirsutus.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Maharashtra (Ranadive et al., 2011) and Kerala
(Mohanan, 2011).
Geastrum sp. (Fig. 2.3g) (Geastraceae Basidiomycotina) (#
MUBSNCKKRSMF-012)
Non-gilled, small, sessile, creamish-white, rounded/bulb on a star
shaped outer wall, grow in trooping groups, annual, humicolous,
infrequent, odour and taste not distinctive and inedible.
Fruit body. At first brownish, coarsely scaly, bulb shaped,
0.6(0.4-0.7) cm diam. (n=5), sessile, thick and brittle. Outer peridium
splitting at maturity into 5 pointed starfish-like rays which reflex back to
reveal the creamy-white inner fleshy layer. Inner peridium (spore sac,
gleba and spore mass) creamish-white, sub-spherical, thin, papery,
sessile and opening by a fringed apical pore.1.4 (1.1-1.8) cm diam.
(n=7).
Gleba (spore mass). At first pallid. Firm and becoming brown
with powdery deposits.
Spores. Spherical, warty and brown, 4-5 µm diam. (n=10).
Substrate. On decomposing leaf litter and twigs of Acacia
mangium and Sapium insigne.
Occurrence. Sacred grove in Maggula and coffee agroforest in
V’Badaga.
Distribution. Not known.
Gymnopilus junonius (Fr.) P.D. Orton (Fig. 2.3e and f) (Strophariaceae
Basidiomycotina) (# MUBSNCKKRSMF-013)
Gilled, medium to large agaric, orange to yellow, dense
caespitose clusters, annual, carbonicolous, rare, odour acidic or bamboo
shoot, taste not distinctive and edible.
Cap. Initially dark orange fades to yellow with age, appressed
fibrillose-squamulose, convex, becoming expanded, plane and wavy and
depression often deepens to the stipe. Flesh concolorous, firm and
medium: 5.2 (2.8-8.2) cm diam. (n= 10).
Gills. Orange brown to creamish yellow, adnate, broad and
crowded.
Spores. Brownish orange, finely warty and ellipsoid: 8 (7.9-8.3)
× 5.4 (5.3-5.9) µm (n=14).
Stipe. Ring absent, pallid ochraceous-brown, more or less equal
or slightly bulged towards the base and fibrillose-striate with scattered
squamules: 4.9 (2.4-8.4) × 0.9 (0.35-1.6) cm (n=10). Flesh yellowish,
firm, stuffed and full.
Substrate. On soil, roots and stumps of burnt decaying Bambusa
sp.
Occurrence. Coffee agroforestry in B’Shettigeri.
85
Distribution. Kerala (Mohanan, 2011).
Ileodictyon gracile Berk. (Fig. 2.3h) (Phallaceae Basidiomycotina) (#
MUBSNCKKRSMF-014)
Non-gilled, small, sessile, white, lattice-like sphere extruding
from a partially submerged egg, grow in troops or solitary, annual,
humicolous, infrequent, odour foul/foetid, taste not distinctive and
inedible.
Fruit body. Initially bone-white, egg-shaped/sub-spherical: 0.7
(0.6-0.8) × 0.5 (0.4-0.6) cm (n=6), attached to the substrate by a
mycelial cord, outer membrane delicate, finely elastic, and closing the
compressed lattice surrounded the white gleba (spore mass). At maturity
the egg ruptures and the spore mass carried upwards on the inside
surface of the bright white lattice: 2.7 cm (1.5- 3.3) × 1.3 cm (1.0-1.6)
diam. (n=6).
Spores. Hyaline, smooth and ellipsoidal: 4.4 (3.3-4.6) × 1.6 (1.3-
1.8) µm (n=10).
Substrate. Rotting sheath of inflorescence of Cocos nucifera and
rotting twigs and leaf litter of Eupatorium odoretum and Pongamia
pinnata.
Occurrence. Reserve forest of Makutta and coffee agroforest of
V’Badaga.
Distribution. Kerala (Mohanan, 2011).
Lentinus dicholamellatus Manim. (Fig. 2.4a and b) (Polyporaceae
Basidiomycotina) (# MUBSNCKKRSMF-015)
Gilled, large, irregular infundibuliform bracket with lateral stipe,
creamish with brownish squamules/tinge, solitary or in groups, annual,
lignicolous, frequent, odour mealy, taste not distinctive and edible with
second preference.
Cap. Upper surface at first pale yellow changing to brownish
orange and densely dotted with very fine appressed or erect squamules.
Initially convex with a depressed centre becoming deeply
infundibuliform, finely striate, radially fibrillose, margin
incurved/inrolled and lobate: 19.3 (25.6- 14.2) cm diam. (n=3). Flesh
creamish, thin, elastic and leathery.
Gills. Yellowish-white, deeply decurrent and crowded.
Spores. Hyaline, smooth and ellipsoidal: 7.7 (7.2-7.9) × 3.8 (3.4-
3.9) µm (n=10).
Stipe. Concolorous with cap, often dotted with erect pointed
squamules, central/eccentric/lateral, almost equal and solid: 4.1 (3.1-4.7)
× 1.3 (1.2-1.3) cm (n=3).
Substrate. Rotting logs of Canarium strictum, Mangifera indica
and Vateria indica.
Occurrence. In Bettoli sacred grove, reserve forest in Makkuta
and coffee agroforest in V’Badaga.
Distribution. Kerala (Mohanan, 2011).
Lentinus patulus Lév. (Fig. 2.4e) (Polyporaceae Basidiomycotina) (#
MUBSNCKKRSMF-016)
86
Gilled, small to medium, infundibuliform with central stipe,
creamish-white with brownish squamules, in small clusters, annual,
lignicolous, infrequent, odour mealy, taste not distinctive and inedible.
Cap. White to cream, with fine brown to blackish squamules
more towards the centre, at first convex with depressed centre, finally
attain infundibuliform, finely sulcate, striate towards margin, margin
regular and thin: 3.8 (2.7-4.9) cm (n=10). Flesh white, thin and at first
weakly elastic becoming more leathery on drying.
Gills. White becoming creamish buff, decurrent, narrow and
moderately crowded.
Spores. Hyaline, smooth and ellipsoidal: 8 (6.6-9.2) × 4.6 (4-5.3)
µm (n=14).
Stipe. Ring absent, concolorous with cap, possess fine blackish
fibrillose squamules, typically central to eccentric, short, more or less
equal, arising from rhizomorph: 1.7 (0.9-3.8) × 0.3 (0.2-0.6) cm (n=10).
Flesh white, firm, tough and thin.
Substrate. On dead stub of Mangifera indica.
Occurrence. Coffee agroforest in B’Shettigeri.
Distribution. Kerala (Mohanan, 2011).
Lenzites vespacea (Pers.) Pat. (Fig. 2.4c and d) (Polyporaceae
Basidiomycotina) (# MUBSNCKKRSMF-017)
Non-gilled, Large, semi-circular or fan-shaped bracket,
creamish-white to brownish-orange, solitary or in limited tires,
perennial, lignicolous, common, odour and taste not distinctive and
inedible.
Fruit body. Upper surface creamish brown with concentric zones
(brown, tan and grey), downy or finely hairy, concentrically grooved and
radially wrinkled, sometimes surface shows algal growth, narrowly
attached and sessile: 15 (10.4-23.4) cm diam. × 1-1.2 cm thick (n=3).
Flesh creamish, leathery and tough.
Pores. Whitish-buff and straw/gill/maize-like in a radial
arrangement with branching.
Spores. Hyaline, broadly ellipsoidal and smooth: 7.8 (5.3-9.2) ×
5.7 (5.3-6.6) µm (n=11).
Substrate. Rotting logs of Acacia mangium, Acrocarpus
fraxinifolius, Artocarpus heterophyllus, A. hirsutus, Lagerstroemia
microcarpa, Syzygium cuminii, Tectona grandis and Toona ciliata.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Maharashtra (Ranadive et al., 2011) and Kerala
(Mohanan, 2011).
Panus conchatus (Bull.) Fr. (Fig. 2.4g and h) (Polyporaceae
Basidiomycotina) (# MUBSNCKKRSMF-018)
Gilled, medium, trumpet-shaped agaric, infundibuliform with
central stipe, brownish-orange, velvety, solitary or in small clusters,
annual, lignicolous, infrequent, odour and taste not distinctive and
inedible.
Cap. Upper surface at first purple redfading to brownish-orange
with age, applanate to depressed, surface striate, velvety, smooth, thin,
leathery, appressed squamules at centre, margin inrolled, lobed and hairy
87
throughout: 8.8 (6.5-10.2) cm diam. (n=5). Lower hymenial surface at
first violet or purple fading to creamish, possess a series of irregular,
blunt gill-like wrinkles and folds and decurrent.
Stipe. Purple-brown, thickly velvety/pubescent throughout,
fading with age, tough, long, solid and more or less equal: 4.6 (3.4-5.8)
× 0.9 (0.6-1.1) (n=5). Flesh creamish-brown, tough, leathery and thin.
Spores. Hyaline, smooth and ellipsoidal: 5.3 (4.6-5.9) × 2.8 (2.6-
3.2) µm (n=12).
Substrate. Rotting logs of Delonix regia, Mangifera indica and
Memecylon umbellatum.
Occurrence. Reserve forest in Sampaje and coffee agroforestry
in B’Shettigeri.
Distribution. Kerala (Mohanan, 2011).
Pleurotus pulmonarius (Fr.) Quél. (Fig. 2.5a & b) (Pleurotaceae
Basidiomycotina) (# MUBSNCKKRSMF-019)
Gilled, small to medium, fleshy, stipe lateral or absent, whitish
becoming creamish, irregular, fan- or bracket-shaped, incaespitose tufts
or groups, annual, infrequent, lignicolous, mealy odour and taste, and
edible.
Cap. Whitish becoming creamish-yellow with age, at first
shallowly convex then flattened, reniform to irregularly flabelliform,
undulating and wavy, lobed as well as split margin, narrowing at point
of attachment, fleshy and smooth: 2.1 (0.8-3.8) cm diam. (n=6). Flesh
white, slightly fibrous and moderate.
Gills. White, becoming creamish, decurrent, narrow and close.
Spores. Hyaline, smooth and ellipsoidal or cylindrical: 8.1 (7.9-
8.6) × 4.9 (4-5.3) µm (n=12).
Stipe. White, lateral or eccentric, very short, slightly woolly,
stout and hard: 0.5 (0.3-0.7) × 0.4 (0.3-0.5) cm (n=6). Flesh white, firm
and full.
Substrate. Rotting twigs of Erythrina subumbrans and Jatropha
curcas.
Occurrence. Coffee agroforestry in B’Shettigeri.
Distribution. Not known.
Polyporus sp. (Fig. 2.5c & d) (Polyporaceae Basidiomycotina) (#
MUBSNCKKRSMF-020)
Porous, small, fan- or kidney-shaped, creamy-brown, solitary,
annual, lignicolous, rare, odour and taste not distinctive and inedible.
Cap. Camouflaged, upper surface creamy with coffee-brown
concentric bands, kidney- or fan shaped, fleshy, shiny, smooth and with
regular margin: 2.6-2.8 cm diam. (n=2). Flesh white, thick and fleshy.
Stipe. Lateral, short, ivory-colour and tough.
Pores. Whitish, irregularly angular, decurrrent and 3.5-4 mm
deep.
Spores. White, fusiform and smooth: 10.7 (9.2-13.2) × 5.4 (5.3-
5.9) µm (n=6).
Substrate. Rotting twigs of Ficus religiosa.
Occurrence. Sacred grove in Maggula.
Distribution. Not known.
88
Figure 2.4. Photographs of macrofungi of Kadagu region.
a and b: Lentinus dicholamellatus on wood; c and d: Lenzites
vespacea on stub; e: Lentinus patulus on stub; f: Ramaria sp. on
soil; g and h: Panus conchatus on twig.
89
Figure 2.5. Photographs of macrofungi of Kadagu region.
a and b, Pleurotus pulmonarius on wood; c and d, Polyporus sp. on
twig; e, Scleroderma verrucosum on soil; f and g, Termitomyces
tylerianus on termite soil; h, Trogia infundibuliformis on twig; i
and j, Tricholoma sp. on soil with woody debris; k, Xylaria longipes
on wood embedded in soil.
90
Ramaria sp. (Fig. 2.4f) (Gomphaceae Basidiomycotina) (#
MUBSNCKKRSMF-021)
Non-gilled, small to medium, coral-like and antler-tip-like, lilac
to creamish, solitary, or in small groups, annual, carbonicolous, rare,
odour and taste not distinctive and inedible.
Fruit body. Lilaceous to creamish, fragile with loose limited
branching and coral-like with pointed forked tips (antler-like). Branches
filiform arising from long slender stipe and dusted with smokes of grey
spores and minutely downy at the base: 5.4 (2.5-9.6) × 1.8 (1.1-2.5) cm
diam. (n=10). Flesh creamish and elastic.
Spores. Fusiform, hyaline and smooth: 10.3 (7.9-13.2) × 5.6 (5.3-
7.9) µm (n=10)
Stipe. Long, slender, fibrous, tough, smooth and equal: 4.6 (2.2-
8.3) × 0.2 (0.2-0.3) cm (n=10).
Substrate. On laterite soil and clay roof tiles.
Occurrence. Clay tiled roofs of coffee agroforest in B’Shettigeri.
Distribution. Not known.
Scleroderma verrucosum (Bull.) Pers. (Fig. 2.5e) (Sclerodermataceae
Basidiomycotina) (# MUBSNCKKRSMF-022)
Non-gilled, medium, knobbly, yellowish-brown, solitary or in
small groups, annual, silvicolous, rare, odour and taste not distinctive,
edible and ectomycorrhizal.
Fruit body. Yellowish-brown, knobby (round headed hammer-
like) and tapered below into a thick grooved hard long stipe-like base:
5.7 (3.8-7.9) × 2.4 (1.8-3.3) cm (n=10). Attached to the soil by a dense
mass of mycelial cord, wall of head/hymenial portion thin, smooth,
brittle and sparsely scaly throughout: 4.3 (3.2-6.6) cm diam. (n-10). On
cracking opens at apex to form an irregular slit for the release/dispersal
of spores.
Spores. Spherical, dark brown and spiny: 11.1 (9.2-13.2) × 10.8
(9.2-13.2) µm (n=10).
Substrate. On soil below the trees of Canarium strictum,
Holigarna nigra and Vateria indica.
Occurrence. Sacred grove in Bettoli and coffee agroforest of
V’Badaga.
Distribution. Kerala (Mohanan, 2011).
Termitomyces tylerianus Otieno (Fig. 2.5f and g) (Lyophyllaceae
Basidiomycotina) (# MUBSNCKKRSMF-023)
Gilled, medium to large agaric, grayish-white, solitary or
occasionally in small groups (3-5), annual, particolous, common, odour
and taste mealy, edible and medicinal.
Cap. Upper surface grayish-white to slightly grayish-yellow,
convex to plane, with a prominent umbo/perforatorium and pointed to
broadly conical(sharply to bluntly umbonate): 9.5 (4.9-14.4) cm diam.
(n=10). Margin straight, smooth, entire and splitting with age. Flesh
white to creamish, thick, smooth and fleshy.
Gills. White, free, crowded and regular.
91
Spores. Hyaline, smooth and broadly ellipsoidal: 7.2 (5.9-9.2) ×
3.8 (3.3-4.7) µm (n=10).
Stipe. White, long, fibrillose, cylindrical with a swollen base and
tapering downwards to a long firm pseudorrhiza: 14.6 (10.2-17.6) × 2.3
(1.2- 4.5) cm (n=10).
Substrate. Termite mounds and soils of grasslands, path of paddy
fields, playgrounds, sacred groves, forests and coffee plantations.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Kerala (Mohanan, 2011).
Tricholoma sp. (Fig. 2.5i and j) (Tricholomataceae Basidiomycotina)
(# MUBSNCKKRSMF-024)
Gilled, medium to large agaric, creamish-brown to potato-brown,
caespitose clusters, annual, silvicolous and lignicolous, rare, odour and
taste mealy and edible.
Cap. Greyish-brown with deposition of fine powder paling
almost wholly after rain to potato/sapota-brown. Initially hemispherical,
becoming campanulate, margin inrolled, smooth and dry: 3.9 (2.8-5.5)
cm diam. (n=10). Flesh white and medium.
Gills. Initially whitish becoming slightly creamish, emarginate
and distant.
Spores. Hyaline, smooth and oval-ellipsoidal: 6.9 (5.3-7.9) × 4.4
(4-5.3) µm (n=12).
Stipe. Long: 9.2 (7.2-11.3) cm tall (n=10), pallid, decorated with
whitish-brown speckled fibrils below ring-zone, bulbose at base: 2.02
(1-2.7) cm diam. (n=10), tapering towards apex: 1.3 (0.7-1.9) cm diam.
(n=10) and ring absent. Flesh white, becoming yellowish with age and
stuffed.
Substrate. On soil rich with debris of Caryota urens.
Occurrence. In reserve forest in Sampaje.
Distribution. Not known.
Trogia infundibuliformis Berk.& Broome (Fig. 2.5h) (Marasmiaceae
Basidiomycotina) (# MUBSNCKKRSMF-025)
Vein-like ridges, small, funnel-shaped, brownish to orange,
solitary or in small groups, annual, lignicolous, infrequent, odour
fungoid, taste not distinctive and inedible.
Cap. Brown to orange, fading with age, deeply infundibuliform,
fleshy, thin, smooth, shiny, surface deeply sulcate and margin wavy and
irregular: 2.6 (1.4-3.3) cm diam. (n=6). Gills absent, lower hymenial
surface orange, possess vein-like ridges and decurrent.
Stipe. Brownish fading with age, smooth, hollow and more or
less equal but slightly bulged at the base or point of attachment to wood:
2.2 (1.5-2.6) × 0.3 (0.2-0.4) cm (n=6). Flesh brownish orange, tough and
thin.
Spores. Hyaline, smooth and ellipsoidal: 7.8 (7.2-8.5) × 4.1 (3.3-
4.6) µm (n=10).
Substrate. On decaying twigs of Coffea robusta.
Occurrence. Sacred grove in Maggula and coffee agroforestry in
V’Badaga.
92
Distribution. Kerala (Kumar and Manimohan, 2009c; Mohanan,
2011).
Xylaria longipes Nitschke (Fig. 2.5k) (Xylariaceae Ascomycotina) (#
MUBSNCKKRSMF-026)
Club-shaped mature fruit body, develops on wood, project above
ground, usually gregarious, common, possess stipe, tough or woody,
annual, odour and taste not distinctive, and medicinal.
Fruit body. Upper stromatal surface black, warty, often
somewhat bent over and narrowing slightly into a brownish-black
sterile.
Stipe. Cylindrical or baseball bat-shaped or clavate and smooth
or slightly downy. Perithecia black, sub-spherical, fully embedded in
stromatal tissue and arranged in a single dense layer just below the
surface towards the apex: 4.8 (2.8-6.1) × 0.7 (0.4-0.8) cm (n=10). Flesh
white and hard.
Asci. Cylindrical: 155.6 (147.3-163.1) × 7.5 (5.5-9) µm.
Spores. Dark brown, smooth, ellipsoid to reniform, flattened on
one side with distinct cleft, non-septate and uniseriate: 13.3 (12.5-14.5)
× 5.9 (5.5-6) µm (n=10).
Substrate. Rotting logs and stumps of Acrocarpus fraxinifolius,
Artocarpus hirsutus, Erythrina subumbrans, Memecylon umbellatum
and Syzygium cumini.
Occurrence. Found in all the locations of sacred groves, reserve
forests and agroforests.
Distribution. Kerala (Mohanan, 2011).
Discussion and outlook
Two megadiversity hotspots in India, the Western Ghats and
Himalayas are the treasures of a variety of life forms and always
fascinating for exploration. Mushrooms especially edible forms are of
immense economic value as alternative food source against plant and
animal food sources. They are versatile as source of adequate protein,
fibre and a variety of bioactive compounds and possess the capacity to
decrease cholesterol level in blood. Besides food source, several
macrofungi serve as medicinal and some are of agricultural importance
as ectomycorrhizal fungi. Interestingly, a wide range of agarics has been
reported from the Nilgiri Biosphere Reserve (Natarajan et al., 2005a)
and ectomycorrhizal fungi from dipterocarp forest stands of Kodagu
region (Natarajan et al., 2005b).
The current study projected several edible, medicinal and one
ectomycorrhizal fungi in one-time survey. Sacred groves and reserve
forests provide fairly undisturbed natural habitats for a variety of
macrofungi. These biomes are the ideal sites for successful conservation
of macrofungi as natural repositories (Brown et al., 2006).
Domestication of desired macrofungi can be achieved in agroforest
consisting of shade-grown commercial plantations (e.g. coffee,
cardamom, cocoa and areca), monocrops (e.g. rubber) and tree-less field
crops (e.g. paddy, sugarcane and banana). Brown et al. (2006) studied
the impact of fragmentation and disturbance on the diversity and
distribution of macrofungi in tropical rain forests of Kodagu region.
They recorded macrofungi during three wet seasons in 25 sacred groves,
93
10 reserve forests and 23 coffee plantations. Based on this long-term
study, they concluded that habitat degradation is an important threat to
macrofungal diversity than fragmentation. Although sacred groves
occupied less area, they are valuable in macrofungal conservation due to
unique habitat with higher abundance of sporocarp as well as
morphospecies compared to reserve forests and coffee-agroforests. On
the contrary, our one-time study revealed the highest species richness in
coffee-agroforests than sacred groves and reserve forests. However,
there may be some difference regarding the abundance of sporocarps of
macrofungi in these habitats and long-term studies may reveal more
improved perception. In shade-grown coffee-agroforests, in addition to
native trees, several exotic tree species are common (e.g. Acacia
mangium, Acrocarpus fraxinifolius, Artocarpus hirsutus, Dalbergia
latifolia, Grevelia robusta,Syzygium cuminiiand Toona ciliata). Besides,
small treespecies are also common (e.g. Erythrina subumbransand
Glyricidia sepium). It is likely, regular pruning of such shade trees as
litter source for coffee plantation and misting during dry seasons might
be responsible for occurrence of macrofungi throughout the year. As
human disturbanceshave to be avoided in sacred groves and reserve
forests, agroforests constitute ideal habitats to domesticate edible,
medicinal and ectomycorrhizal fungi for economic growth. Similar to
flora and fauna, macrofungi also consititutes another important link in
forest ecosystems as detritus decomposers. But, knowledge on the
diversity, distribution of mcrofungi and impact of forest
degradation/fragmentation on macrofungi is insufficient. Rehabilitation
of many forest communities needs considerable time especially
macrofungiprefers old-growth forests than the new forests for their
perpetuation (Norden and Appelqvist, 2001). For instance,distinct
succession pattern of ectomycorrhizal fungi was seen in old (1117
years) and young (37 years) dipterocarp forests in Kodagu region
(Natarajan et al., 2005b). Besides plant detritus and pure forest stands
(e.g. dipterocarp and bamboo groves), there are several ecological niches
deserve meticulous attention to explore macrofungi in the Western
Ghats: coprophilus fungi on the dung of wild animals (e.g. Amanita,
Entoloma and Xylaria), medicinally valuable entomopathogens (e.g.
Cordyceps and Ophiocordyceps) and termite mounds for edible
mushrooms (e.g. Termitomyces).
Each geographical location has specific characteristic features
and yield of optimum number of macrofungi depends on the time and
frequency of field survey (Halme and Kotiaho, 2012). For each biome in
a location, it is necessary to earmark substrate, time and frequency of
sampling for maximum recovery of macrofungi. In addition, phase-wise
long-term studies on macrofungi are warranted for a comprehensive and
total understanding of the diversity in different parts of the Western
Ghats to improve ourknowledge on the species richness, functional
diversity, conservation strategies and economic benefits. Traditional
knowledge of local people and tribals should not be ignored to fill the
gaps in our knowledge on the value of macrofungi.
94
Acknowledgement
Authors are thankful to Mangalore University for permission to
carry out this study in the Department of Biosciences.
References
Abrar, S., Swapna, S. and Krishnappa, M. 2007. Dictyophora
cinnabarina. Current Science 92, 12191220.
Bhagwat, S., Kushalappa, C., Williams, P. and Brown, N. 2005. The role
of informal protected areas in maintaining biodiversity in the
Western Ghats of India. Ecology and Society 10, article # 8, 1-
40: http://www.ecologyandsociety.org/vol10/iss1/art8/
Brown, N., Bhagwat, S. and Watkinson, S. 2006.Macrofungal diversity
in fragmented and disturbed forests of the Western Ghats of
India. Journal of Applied Ecology 43, 1117.
Das, K. 2010. Diversity and conservation of wild mushrooms in Sikkim
with special reference to Barsey Rhododendron Sanctuary.
NeBIO 1, 113.
Halme, P. and Kotiaho, J.S. 2012.The importance of timing and number
of surveys in fungal biodiversity research. Biodiversity and
Conservation 21, 205219.
Hawksworth, D.L. 2001.The magnitude of fungal diversity: the 1.5
million species estimate revisited. Mycological Research 105,
14221432.
Hawksworth, D.L. 2012. Global species numbers of fungi: Are tropical
studies and molecular approaches contributing to a more robust
estimate? Biodiversity and Conservation 21, 24252433.
Jha, K.S., Kumar, V. Tripathi, N.N. 2011.Survey of ethnomedicinal
macrofungi of Nagarjuna and Phulchowki areas of Kathmandu
Valley, Nepal. Internal Journal of Pharmaceutical Sciences
Review and Research11, 147151.
Johnsy, G., Sargunam, S.D., Dinesh, M.G. and Kaviyarasan, V. 2011.
Nutritive value of edible wild mushrooms collected from the
Western Ghats of Kanyakumari district. Botany Research
International 4, 6974.
Jordan, M. 1995. The Biology of Higher Fungi: The Encyclopedia of
Fungi of Britain and Europe. David and Charles Publishers, UK,
p. 384.
Kibby, G. 1979. Mushrooms and Toadstools a Field Guide. Oxford
University Press, Oxford, UK, p.256.
Kumar, T.K. and Manimohan, P. 2009a.The genus Lepiota (Agaricales,
Basidiomycota) in Kerala State, India. Mycotaxon 107, 105138.
Kumar, T.K. and Manimohan, P. 2009b.The genera Leucoagaricus and
Leucocoprinus (Agaricales, Basidiomycota) in Kerala State,
India. Mycotaxon 108, 385428.
Kumar, T.K. and Manimohan, P. 2009c.Rediscovery of Trogia cyanea
and a record of T. infundibuliformis (Marsmiaceae, Agaricales)
from Kerala State, India. Mycotaxon 109, 429436.
Kushalappa, C.G.and Bhagwat, S. 2001. Sacred groves: biodiversity,
threats and conservation, In: Forest Genetic Resources: Status,
Threats, and Conservation. Shaankar, U.R., Ganeshaiah, K.N.
and Bawa, K.S. (Ed.), Oxford and IBH, New Delhi, pp. 2129.
95
Leelavathy, K.M., Manimohan, P. and Arnolds, E.J.J. 2006.Hygrocybe
in Kerala State, India. Persoonia 19, 101151.
Manoharachary, C., Sridhar, K.R., Singh, R., Adholeya, A.,
Suryanarayanan, T.S., Rawat, S. and Johri, B.N. 2006.Fungal
biodiversity: Distribution, conservation and prospecting of fungi
from India. Current Science 89, 5871.
Mohanan, C. 2011. Macrofungi of Kerala. Kerala Forest Research
Institute, Hand Book # 27, Kerala, India, p. 597.
Natarajan, K., Narayanan, K., Ravindran, C. and Kumaresan, V.
2005a.Biodiversity of agarics from Nilgiri Biosphere Reserve,
Western Ghats, India. Current Science 88, 18901893.
Natarajan, K., Senthilarasu, G., Kumaresan, V. and Riviere, T.
2005b.Diversity in ectomycorrhizal fungi of a dipterocarp forest
in Western Ghats. Current Science 88, 18931895.
Norden, B. and Appelqvist, T. 2001. Conceptual problems of ecological
continuity and its bioindicators. Biodiversity and
Conservation10, 779791.
Pascal, J.P., and Meher-Homji,V.M. 1986.Phytochorology of Kodagu
(Coorg) district, Karnataka. Journal of Bombay Natural History
Society 83, 4356.
Purkayastha, R.P. and Chandra, A. 1985.Manual of Indian Edible
Mushrooms. Today and Tomorrow’s Printers and Publishers,
New Delhi, p. 267.
Puttaraju, N.G., Venkateshaiah, S.U., Dharmesh, S.M., Urs, S.M.N. and
Somasundaram, R. 2006. Antioxidant activity of indigenous
edible mushrooms. Journal of Agricultural and Food Chemistry
54, 97649772.
Ranadive, K.R., Vaidya, J.G., Jite, P.K., Ranade, V.D., Bhosale, S.R.,
Rabba, A.S., Hakimi, M., Deshpande, G.S., Rathod, M.M.,
Forutan, A., Kaur, M., Naik-Vaidya, C.D., Bapat, G.S. and
Lamrood, P. 2011. Checklist of Aphyllophorales from the
Western Ghats of Maharashtra State, India. Mycosphere 2, 91
114.
Riviere, T., Diedhiou, A.G., Diabate, M., Senthilarsu, G., Natarajan, K.,
Verbeken, A., Buyck, B., Dreyfus, B., Bena, G. and Ba, A.M.
2007.Genetic diversity of ectomycorrhizal basidiomycetes from
African and Indian tropical rain forests. Mycorrhiza 17, 415428.
Sargunum, S.D., Johnsy, G., Samuel, A. and Kaviyarasan, V.
2012.Mushrooms in the food culture of the Kaani tribe of
Kanyakumari district. Indian journal of Traditional Knowledge
11, 150153.
Selvam, K., Priya, M.S., Sivaraj, C. and Arungandhi, K. 2012.
Identification and screening of wood rot fungi from Western
Ghats area of South India. International Journal of ChemTech
Research 4, 379388.
Swapna, S., Abrar, S. and Krishnappa, M. 2008.Diversity of macrofungi
in semi-evergreen and moist deciduous forest of Shimoga
District - Karnataka, India. Journal of Mycology and Plant
Pathology 38, 2126.
Thiribhuvanamala, G., Prakasam, V., Chandrasekar, G., Sakthivel, K.,
Veeralakshmi, S., Velazhahan, R. and Kalaiselvi, G.
2011.Biodiversity, conservation and utilization of mushroom
96
flora from the Western Ghats region of India. Proceedings of the
7th International Conference on Mushroom Biology and
Mushroom Products, pp. 163172.
Thomas, K.A., Hausknecht, A. and Manimohan, P. 2001. Balbitiaceae of
Kerala State, India: New species and new and noteworthy
records. Österreichische Zeitschrift für Pilzkunde 10, 87114.
... Most of the diversity studies pertaining to macrofungi of Peninsular India are confined to the Western Ghats (e.g. Bhagwat et al., 2005;Manoharachary et al., 2005;Natarajan et al., 2005aNatarajan et al., , 2005bBrown et al., 2006;Swapna et al., 2008;Mohanan, 2011;Karun et al., 2014;Usha and Janardhana, 2014), while coastal regions especially CSDs and mangroves are ignored. Similar to other fungi, macrofungal occurrence and diversity is also dependent on the detritus generated by the psammophytes in CSDs and mangroves. ...
Chapter
Full-text available
Although coastal sand dunes (CSDs) and mangroves are important biogeographic ecological zones in India, they are threatened due to human interference (encroachment, urbanization, sand mining and fishery activities). This chapter projects occurrence of macrofungi in CSDs and mangroves based on surveys in Dakshina Kannada (Karnataka State) during monsoon season (June–October). A brief description of fourteen macrofungi based on field and laboratory observations along with their extent of occurrence, substrate preference and commercial value is given. Some macrofungi occurring on the CSDs and mangroves are edible and dependent on sandy/silty soils, leaf litter, woody litter and herbivore dung (e.g. Coprinus plicatilis, Lycoperdon decipiens and Termitomyces schimperi). Some are ectomycorrhizal in CSDs or in mangroves (Collybia fusipes, Inocybe petchii and Lycoperdon decipiens). This study as well as earlier observations revealed occurrence of several edible, medicinal and mycorrhizal macrofungi in CSDs and mangroves. Currently, CSDs and mangroves are highly neglected and it is necessary to safeguard, promote and utilize macrofungal resources as social and cultural heritage of coastal dwellers. Keywords: Coastal sand dunes, Mangroves, Diversity, Macrofungi, Mushrooms, Ectomycorrhizae
... The fire-damaged cashew plantation adjacent to the scrub jungle showed preponderance of Gymnopilus sp. on partially burnt woody litter (Karun & Sridhar 2014a). In bamboo thickets, Gymnopilus junonius was predominant on the burnt soil as well as on partially burnt wood (Karun et al. 2014). Although G. junonius was not dominant in our study, it was restricted to burnt soil in fire-impacted region. ...
Article
Full-text available
Fortnightly survey in control and fire-impacted regions of scrub jungle of south-west coast of India during south-west monsoon (50 m2 quadrats up to 10 weeks) yielded 34 and 25 species of macrofungi, respectively. The species as well as sporocarp richness were the highest during the fourth week, while the diversity attained the highest during the second week in control region. In fire-impacted region, the species and sporocarp richness and diversity peaked at sixth week. Seven species common to both regions were Chlorophyllum molybdites, Lepiota sp., Leucocoprinus birnbaumii, Marasmius sp. 3, Polyporus sp., Schizophyllum commune and Tetrapyrgos nigripes. The overall sporocarp richness was higher in fire-impacted than in control region. The Jaccard’s similarity between regions was 13.5%, while fortnights of regions ranged from 0% (10th week) to 11.7% (eighth week). Control region showed single-species dominance by Xylaria hypoxylon, while multispecies dominance by Cyathus striatus and Lentinus squarrosulus in fire-impacted region. Except for air temperature, nine abiotic factors significantly differed between control and fire-impacted regions. The Pearson correlation was positive between species richness and phosphorus content in fire-impacted region (r = 0.696), while sporocarp richness was negatively correlated with pH in control region (r = −0.640). Economically viable species were 12 and 10 without overlap in control and fire-impacted regions, respectively. Keywords: Mushrooms, diversity, abiotic factors, substrate, disturbance
Article
Full-text available
This inventory focused on the diversity of macrofungi in an arboretum and three plantations (Acacia, Areca and cashew) of the southwest coast of India during monsoon (JuneSeptember) and early post-monsoon (OctoberNovember) seasons. A total of 79 macrofungi in 53 genera was recovered from 15,000 m2. The macrofungal species richness was higher in arboretum compared to plantations (30 vs. 1722 species). The highest number of macrofungi were confined to the arboretum than the plantations (25 vs. 1421 species), so also the core-group species (≥10 sporocarps/quadrat) (9 vs. 26 species). The richness of species as well as sporocarps were highest during June and decreased towards November. The macrofungal diversity was highest in Areca plantation and during monsoon period (August/September). Low species similarity was seen between the arobretum and plantations (012.8%), while the similarity increased from June through November (3.642.9%). About 50% of macrofungi possess economic value as ectomycorrhizal (25 species), edible (17 species) and medicinal (10 species). This survey revealed the macrofungal dependence on type of location and vegetation gives scope for their beneficial management. Key words – Arboretum – diversity – macrofungi – plantations – South Indian coast
Article
Full-text available
This study presents results of macrofungal inventory in the Western Ghat forest of Karnataka (reserve forest, shola forest, sacred grove and coffee agroforest) during wet season (JuneNovember). A total of 157 species belonging to 87 genera was recovered. A maximum of 53 species was found in the coffee agroforest with highest diversity, exclusive (confined to a specific forest: 42 sp.) and core-group (frequency of occurrence, 10%: 17 sp.) species. Irrespective of forest, the species richness attained peaks during June and September. Rarefaction indices of species against sporocarps also showed the highest expected number of species in coffee agroforest. Of a total of 9256 sporocarps, the coffee agroforest consists of highest sporocarps than other forests (3715 vs. 16762999). Two-way ANOVA revealed significant spatial difference in richness of species (P < 0.01) as well as sporocarps (P < 0.05) without significant difference temporally. Low species similarity among forests surveyed (2.48.5%) depicts uniqueness of macrofungi in these forests. This survey yielded 45 new records to the Western Ghats and 47 economically valuable core-group fungi (edible, medicinal and ectomycorrhizal). Maintenance of suitable edaphic conditions along with enrichment organic matter (woody and leaf litter) in coffee agroforests seems to maximize economically viable macrofungi. Keywords: diversity, forests, macrofungi, mushrooms, Western Ghats
Article
Full-text available
Nine species of Xylaria (X. escharoidea, X. filiformis, X. hypoxylon, X. longipes, X. multiplex, X. nigripes, X. obovata, X. polymorpha and X. symploci) were recorded during an inventory of various habitats of the Western Ghats and west coast of India. Xylaria escharoidea, X. hypoxylon and X. longipes were common to the Western Ghats and west coast, while five (X. filiformis, X. multiplex, X. obovata, X. polymorpha and X. symploci) and one (X. nigripes) species were confined to the Western Ghats and west coast regions, respectively. Xylaria longipes, X. multiplex, X. obovata and X. polymorpha grew on dead logs/stubs, X. escharoidea, X. nigripes and X. symploci preferred to grow on soil/termite mound/soil embedded with wood, X. hypoxylon preferred to grow on pods/kernels/twigs/humus/wood pieces and X. filiformis exclusively grew on leaves. Xylaria filiformis and X. multiplex recorded for the first time from the Western Ghats. Based on the occurrence on different substrates, a dichotomous key has been given for identification of nine species recorded in this survey. Including this survey, a total of 24 species of Xylaria has been reported from the Western Ghats and west coast regions of Maharashtra, Karnataka, Kerala and Tamil Nadu.
Article
Nine species of Xylaria (X. escharoidea, X. filiformis, X. hypoxylon, X. longipes, X. multiplex, X. nigripes, X. obovata, X. polymorpha and X. symploci) were recorded during an inventory of various habitats of the Western Ghats and west coast of India. Xylaria escharoidea, X. hypoxylon and X. longipes were common to the Western Ghats and west coast, while five (X. filiformis, X. multiplex, X. obovata, X. polymorpha and X. symploci) and one (X. nigripes) species were confined to the Western Ghats and west coast regions, respectively. Xylaria longipes, X. multiplex, X. obovata and X. polymorpha grew on dead logs/stubs, X. escharoidea, X. nigripes and X. symploci preferred to grow on soil/termite mound/soil embedded with wood, X. hypoxylon preferred to grow on pods/kernels/twigs/humus/wood pieces and X. filiformis exclusively grew on leaves. Xylaria filiformis and X. multiplex recorded for the first time from the Western Ghats. Based on the occurrence on different substrates, a dichotomous key has been given for identification of nine species recorded in this survey. Including this survey, a total of 24 species of Xylaria has been reported from the Western Ghats and west coast regions of Maharashtra, Karnataka, Kerala and Tamil Nadu.
Article
Full-text available
2014 – A preliminary study on macrofungal diversity in an arboretum and three plantations of the southwest coast of India. Current Research in Environmental & Applied Mycology 4(2), 173–187, Doi 10.5943/Cream/4/2/5 Abstract This inventory focused on the diversity of macrofungi in an arboretum and three plantations (Acacia, Areca and cashew) of the southwest coast of India during monsoon (JuneSeptember) and early post-monsoon (OctoberNovember) seasons. A total of 79 macrofungi in 53 genera was recovered from 15,000 m 2 . The macrofungal species richness was higher in arboretum compared to plantations (30 vs. 1722 species). The highest number of macrofungi were confined to the arboretum than the plantations (25 vs. 1421 species), so also the core-group species (≥10 sporocarps/quadrat) (9 vs. 26 species). The richness of species as well as sporocarps were highest during June and decreased towards November. The macrofungal diversity was highest in Areca plantation and during monsoon period (August/September). Low species similarity was seen between the arobretum and plantations (012.8%), while the similarity increased from June through November (3.642.9%). About 50% of macrofungi possess economic value as ectomycorrhizal (25 species), edible (17 species) and medicinal (10 species). This survey revealed the macrofungal dependence on type of location and vegetation gives scope for their beneficial management. Introduction Fungi are the most diverse group evolved parallel to plants and animals involve in several ecological services like organic matter decomposition, biogeochemical cycles and symbiotic association. They are capable to occupy and flourish in a variety of ecological niches due to their diversity, distribution, dissemination and adaptability. Although various estimates of fungi range between 0.5 and 9.9 million species, currently 1.53 million species has been accepted based on the plant-fungus ratio in different geographical regions (Cannon 1997, May 2000, Hawksworth 2001, 2012, Mueller & Schmit 2007). However, the recent fungal community analysis by molecular methods gave an estimate of 5.1 million species, which stands as median value of previous conventional range (0.59.9 million) (O'Brien et al. 2005). Now-a-days, macrofungal investigations are gaining tremendous importance owing to the economic benefits especially nutritional and bioactive potential (De Silva et al. 2013, Manna & Roy 2014). Estimated total macrofungi represents about 56,700 species worldwide and up to 850 species are known mainly from the Himalaya and Western Ghats of India (Manoharachary et al. 2006, Mueller et al. 2007). However, recent checklists
Article
Full-text available
Shimoga district is one of the richest floristic area, located in between 13º 27' and 14º 39' N lat and 74º 38' and 76º 34' E long with a wide range of ecosystems and species diversity. Studies on the taxonomy and diversity of macrofungi are gaining importance, as many macrofungi are becoming extinct and facing threat of extinction because of habitat destruction. The current study deals with the diversity of macrofungi in semi-evergreen and moist deciduous forest of Shimoga district Karnataka. The average rainfall is 140 cm, temp is 25C and RH is 60 to 100%. The macrofungal diversity is very rich due to litter decomposition. Surveys were conducted from April 2005 to June 2007 in 10 sampling stations, five of their in semi-evergreen and its remaining five in moist deciduous forest. A total of 100 transects (50 each in semi-evergreen and moist deciduous) were studied each measuring 50 x 20 m. The macrofungi were collected, characterized, allotted accession number, preserved and all the collected specimens were photographed. A total of 778 species of macrofungi belonging to 43 families, 101 genera were enumerated of which 242 species were identified to genus level and 73 were identified to species level. Some of the currently identified genera are Agaricus sp. Xylaria polymorpha. Among the collected species Laccaria sp. forms most denser (D=15.36), abundant (Ab=256) and frequency (F=0.06) in semi-evergreen forest and Schizophyllum sp. forms the most denser (D=16.48), abundant (Ab=164.8) and frequency (F=0.1) in moist deciduous forest. The Shannon diversity index and Simpson index were calculated to be 5.57 and 1.12 in semi-evergreen forest, which indicates the very high species richness of the study site. In moist deciduous forest, the Shannon diversity index was 5.42 and the Simpson index was 0.011. Further investigation is in progress.
Article
Full-text available
The nutritional value of 10 edible mushroom species were analyzed, which forms a part of the food culture of the Kaani tribal community settled in the forests of Kanyakumari district in Tamil Nadu. Young and matured carpophores of 10 common wild edible mushrooms were collected from different locations in the Western Ghats of Kanyakumari district. These mushrooms were analyzed for proximate analysis of nutritional values. The macro nutrient profiles in general revealed that the wild mushrooms were rich sources of protein and carbohydrates and had a low amount of fat. The results showed that the samples contained appreciable amount of essential nutrients. Harvesting of sporophores and conducting inquiries among the tribal people allowed to record 10 taxa of edible mushrooms. For each specimen, local and vernacular names were noted. Hence, these nutrient contents revealed that mushrooms were low energy, healthy food and may also be used as a protein supplementary diet.
Article
Full-text available
Fifty six samples were collected from Western Ghats area, of Tamilnadu and Karnataka, South India. The collected fungi were isolated and identified based on the key provided previously. Phanerochaete chrysosporium-787 was obtained from Microbial Type Culture Collection, Chandigarh, India and was used as the reference fungus. The fungi were screened for their ligninolytic activity based on their ability to oxidize dyes, poly R-478 and remazol brilliant blue, to degrade native lignin and further confirmation was done by the liberation of ethylene from KTBA (2-keto-4-thiomethyl butyric acid). The color removals in 57 samples were in the range of 11.5 to 38.4% in poly-R dye and 11.1 to 72.0 % in remazol brilliant blue. The mycelial growth rates were in the range of 1.24 to 3.67 mg/day and percent degradation of lignin were found to be in the range 20.4 to 68.8. The ligninolytic activity of the fungi were further confirmed by their ability to release ethylene from KTBA and the results were found to be in the range of 1.210 to 3.121 ppm. From the above screening results three best wood rot fungi Polyporus hirsutus, Daedalea flavida, Phellinus sp1 were selected for further studies.
Article
Full-text available
Wild mushrooms have manifold impacts in biology, ecology and economy. They have been a part of our daily life since time immemorial. Apart from their importance as a source of food for the regional poor and as mycorrhizal partners of host trees, some are huge sources of bioactive compounds showing medicinal importance. In the present communication, 126 wild mushrooms collected from Barsey Rhododendron Sanctuary of the state Sikkim are enlisted with their scientific names, common names, distribution, growing period and status of edibility. Medicinally important 46 mushrooms are also highlighted with their medicinal properties. Factors causing their continuous declination are mentioned along with the possible in-situ and ex-situ conservation measures.
Article
Full-text available
Twenty-two taxa belonging to the agaric genus Lepiota are documented from Kerala State, India, including full descriptions and illustrations of eight new species and one new variety (L. ananya, L. anupama, L. babruka, L. babruzalka, L. harithaka, L. nirupama, L. shveta, L. zalkavritha, L. brevipes var. distincta). Of the eleven species that are new records for India, Lepiota subincarnata, L. brevipes, L. elaiophylla, L. ianthinosquamosa and L. murinocapitata are also reported for the first time from Asia. A key to the species of Lepiota in Kerala is given.
Article
Full-text available
Recent estimates of the global species numbers of fungi suggest that the much-used figure of 1.5 million is low, and figures up to 5.1 million have been proposed in the last few years. Data emerging from tropical studies, and from large-scale sequencing of environmental samples, have the potential to contribute towards a more robust figure. Additional evidence of species richness is coming from long-term studies of particular non-tropical sites, and also from molecular phylogenetic studies revealing extensive cryptic speciation. However, uncertainties remain over fungus:plant species ratios and how they should be extrapolated to the global scale, and also as to the geographical distribution of fungi known only as sequences. Also unclear is the extent to which figures should be modified to allow for insect-associated fungi. The need for comprehensive studies, especially in the tropics, to address the uncertainties used in past extrapolations, is stressed. For the present, it is recommended that the phrase “at least 1.5, but probably as many as 3 million” be adopted for general use until some of the current uncertainties are resolved.
Article
India is inhabited by over 50 million tribals belonging to 550 communities and in Tamil Nadu 36 tribal communities live, while six tribal communities are found in the Southernmost Kanyakumari district. Of the six tribes, Kaani tribe lives in the forests and hills of the Western Ghats. The Kaani tribe lives in consonance with Nature and their life is linked to the forest ecosystem. Though they live in settled areas, they still retain the traditional hunter-gatherer instinct, and collect their food from the forests that include mushrooms. Mushrooms contain a host of defense potentiators, which stimulate the immune system of humans. These mushrooms provide rich resources for the gene banks.