scholarly journals Assessment of threat status of the holly fern Cyrtomium micropterum (Kunze) Ching (Polypodiopsida: Dryopteridaceae) in India using IUCN Regional guidelines

2021 ◽  
Vol 13 (1) ◽  
pp. 17554-17560
Author(s):  
C. Bagathsingh ◽  
A. Benniamin

During the field survey in central Western Ghats of India, an interesting dryopteridoid fern species was collected from Nellikathrupodu Range of Billigiri Rangaswamy Temple (BRT) Tiger Reserve of Karnataka.  After a critical study of literature, the specimen was identified as Cyrtomium micropterum (Kunze) Ching.  In India, this species is known only from its type locality Nilgiri and Palani hills of Tamil Nadu.  The present collection from the BRT Tiger Reserve shows its extended distribution and forms the first report for the state of Karnataka.  The present paper deals with the assessment and conservation status of Cyrtomium micropterum (Kunze) Ching in India in accordance with IUCN guidelines for the application of Red List Criteria at regional and national Levels, 2012, Version 4.0.  Detailed descriptions, photographs, microphotographs are provided for easy identification of this species.

Zootaxa ◽  
2020 ◽  
Vol 4881 (2) ◽  
pp. 383-392
Author(s):  
GURUSAMY RAMESH ◽  
RAJAPPA BABU ◽  
KUMARAPURAM A. SUBRAMANIAN

Soa papanasam sp. nov. is described and illustrated based on both sexes from Kalakkad Mundanthurai Tiger Reserve and Meghamalai Wildlife Sanctuary, Tamil Nadu, India. It differs from all other known species of Soa, by hindwing vein R1 originating proximal to vein M1 and distal to M2. This is the first species of the genus Soa described from India.


2005 ◽  
Vol 20 (12) ◽  
pp. 2100-2107 ◽  
Author(s):  
Dunston P. Ambrose ◽  
D. Senthil Raj

Author(s):  
D. W. Minter

Abstract A description is provided for Fomes fomentarius. Sporophores of this fungus are found on both living and dead trees, where the fungus causes a decay of heartwood. Some information on its associated organisms and substrata, dispersal and transmission, habitats and conservation status is given, along with details of its geographical distribution (Africa (São Tomé and Principe, Somalia, Tunisia), Asia (Azerbaijan, China (Hong Kong), Cyprus, Georgia, India (Himachal Pradesh, Jammu & Kashmir, Karnataka, Meghalaya, Sikkim, Tamil Nadu, Uttarakhand, Uttar Pradesh, West Bengal), Iran, Japan, Kazakhstan (Akmola, Aktobe, Almaty, East Kazakhstan, Kostanay, North Kazakhstan, Pavlodar, South Kazakhstan, West Kazakhstan), Kyrgyzstan, Mongolia, Nepal, North Korea, Pakistan, Russia (Altai Krai, Altai Republic, Buryatia, Chelyabinsk Oblast, Irkutsk Oblast, Khabarovsk Krai, Novosibirsk Oblast, Primorsky Krai, Sakha Republic, Sakhalin Oblast, Tyumen Oblast, Zabaykalsky Krai), South Korea, Tajikistan, Turkey, Uzbekistan), Central America (Panama), Atlantic Ocean (Portugal (Madeira)), Europe (Andorra, Austria, Belarus, Belgium, Bosnia and Herzegovina, Bulgaria, Croatia, Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Ireland, Italy, Kosovo, Latvia, Luxembourg, Moldova, Netherlands, Norway, Poland, Portugal, Romania, Russia (Komi Republic, Krasnodar Krai, Moscow Oblast, Nizhny Novgorod Oblast, Orenburg Oblast, Republic of Karelia, Saratov Oblast, Voronezh Oblast), Serbia, Slovakia, Slovenia, Spain, Sweden, Switzerland, Ukraine, UK), North America (Canada (Alberta, British Columbia, Manitoba, New Brunswick, Newfoundland and Labrador, Ontario, Quebec, Saskatchewan), USA (Alabama, Alaska, California, Connecticut, District of Columbia, Florida, Idaho, Iowa, Kentucky, Maine, Massachusetts, Michigan, Minnesota, Montana, Nebraska, New Hampshire, New Jersey, New York, North Carolina, Ohio, Oregon, Pennsylvania, Rhode Island, South Dakota, Tennessee, Vermont, Virginia, Washington, West Virginia, Wisconsin)), South America (Brazil (Minas Gerais, Santa Catarina), Chile)).


Author(s):  
V. P. Hayova

Abstract A description is given for Gloniopsis praelonga. Some information on its dispersal and transmission and conservation status is given, along with details of its geographical distribution (Kenya, Morocco, South Africa, Zambia, Canada (British Columbia), Mexico, USA (Alabama, California, Florida, Illinois, Louisiana, Maryland, Massachusetts, Michigan, Nebraska, New Jersey, New Mexico, New York, North Carolina, Pennsylvania, Texas, Virginia), Argentina, Chile, Ecuador, China (Hubei), India (Karnataka, Tamil Nadu), Pakistan, Taiwan, Azores, Australia (Australian Capital Territory, Queensland), New Zealand, Papua New Guinea, Austria, Belgium, Denmark, France, Gibraltar, Germany, Greece, Irish Republic, Italy, Lithuania, Netherlands, Norway, Portugal, Russia (Leningradskaya oblast), Spain and UK), hosts (Acacia filiculoides, Acacia mearnsii, Acacia sp., Acer campestre, Acer pseudoplatanus, Acer sp., Alnus sp., Andromeda sp., Arbutus menziesii, Arbutus unedo, Arctostaphylos tracyi, Arctostaphylos sp., Aronia sp., Arundo donax, Atalantia sp., Azalia sp., Bambusa sp., Poaceae, Berchemia scandens, Berchemia sp., Betula pendula, Betula sp., Buddleja sp., Buxus sempervirens, Calicotome spinosa, Calluna vulgaris, Carya tomentosa, Carya sp., Castanea sativa, Castanea sp., Catalpa bignonioides, Catalpa sp., Ceanothus sp., Chamaerops sp., Cistus salviifolius, Cistus sp., Cladium jamaicense, Coccoloba ewifera, Combretum zeyheri, Combretum sp., Cornus sp., Corylus avellana, Corylus colurna, Corylus sp., Crataegus laevigata, Crataegus monogyna, Crataegus sp., Duvaua longifolia, Erica arborea, Ericaceae indet., Eucalyptus coccifera, E. globulus, Eucalyptus sp., Fagus sylvatica, Fagus sp., Francoa sonchifolia, Rhamnus frangula, Fraxinus excelsior, Fraxinus ornus, Fraxinus sp., Poaceae indet., Hedera helix, Hedera sp., Hippophae rhamnoides, Ilex aquifolium, Ilex sp., Jasminum sp., Juglans cinerea, Juniperus sp., Lavandula stoechas, Leucothoe axillaris, Ligustrum japonicum, Ligustrum vulgare, Ligustrum sp., Lithocarpus sp., Lonicera periclymenum, Lonicera sp., Malus sylvestris, Malus sp., Melia azedarach, Metrosideros robusta, Myrica gale, Myrtus communis, Ostrya sp., Prunus persica var. persica, Phormium tenax, Phragmites australis, Pinus halepensis, Pinus pinaster, Pinus sylvestris, Pinus sp., Pittosporum sp., Plantae indet., Populus alba, Populus sp., Prunus spinosa, Prunus sp., Malus domestica, Malus fusca, Quercus agrifolia, Q. alba, Q. ilex, Q. petraea, Q. robur, Quercus sp., Rhamnus sp., Rhododendron ponticum, Rhododendron sp., Robinia pseudoacacia, Robinia sp., Rosa arvensis, Rosa canina, Rosa sp., Rosaceae indet., Rubus fruticosus, Rubus idaeus, Rubus inermis, Rubus sp., Sabal palmetto, Salix caprea, Salix fragilis, Salix sp., Sambucus nigra, Sambucus sp., Sequoia sp., Serenoa repens, Smilax aspera, Sorbus sp., Spiraea canescens, Spiraea sp., Symphoricarpos albus, Trachycarpus fortunei, Ulex europaeus, Ulex sp., Ulmus procera, Ulmus sp., Vaccinium glabrum, Vaccinium vitis-idaea, Vaccinium sp., Verbascum sp., Viburnum lantana, Viburnum opulus, Viburnum sp., Vitis vinifera subsp. sylvestris, Vitis sp., Xanthorrhoea sp. and Xolisma ferruginea) and associated fungi (Actinocladium rhodosporum, Ascochyta deformis, Circinotrichum olivaceum, Clypeosphaeria mamillana, Dasyscypha cerina, Farlowiella carmichaeliana, Glonium lineare, Herpotrichiella sp., Hysterium angustatum, Keissleriella caudata, Lophiostoma ulicis, Metasphaeria longispora, Orbilia alnea, Phaeostalagmus cyclosporus, Lophiostoma compressum, Pleospora sp., Pseudospiropes obclavatus, Strossmayeria atriseda, Strossmayeria bakeriana, Sporothrix ghanensis, Taeniolina scripta, Valsa ceratophora and Zygosporium gibbum).


Author(s):  
D. W. Minter

Abstract A description is provided for Clonostachys candelabrum, usually found on pine debris (typically dead, wet and blackened needles, twigs and cones attached to trash). Some information on its morphology, habitat, dispersal and transmission and conservation status is given, along with details of its geographical distribution (Cote d'Ivoire, Kenya, South Africa, USA (District of Columbia, Louisiana, Maryland, New Jersey, Washington), Brazil (Pernambuco), Chile, Venezuela, India (Andhra Pradesh, Arunachal Pradesh, Bihar, Karnataka, Kerala, Maharashtra, Rajasthan, Madhya Pradesh, Tamil Nadu, Uttar Pradesh), Japan, Korea Republic, Syria, Thailand, Uzbekistan, Spain (Canary Islands), Australia (Australian Capital Territory), New Zealand, Cuba, Puerto Rico, Belarus, Belgium, Germany, Italy, France, Netherlands, Portugal, Russia (Leningrad Oblast, Samara Oblast, Tver Oblast), Spain, Switzerland, Ukraine and UK) and host (Pinus sylvestris).


2018 ◽  
Vol 17 (1) ◽  
pp. 21
Author(s):  
Arun Kanagavel ◽  
Sethu Parvathy ◽  
Abhiijth P. Chundakatil ◽  
Neelesh Dahanukar ◽  
Benjamin Tapley

Distribution and habitat associations of the Critically Endangered frog Walkerana phrynoderma (Anura: Ranixalidae), with an assessment of potential threats, abundance, and morphology. Little is known about Walkerana phrynoderma, a frog endemic to the Anamalai Hills of the Western Ghats of India. Baseline information (i.e., distribution, threats, habitat characteristics, activity patterns, and relative abundance) is provided for this species, with the aim of improving our understanding of the status of the species in the wild. Visual-encounter, transect, and time-activity budget surveys were conducted in and around the Anamalai Hills of the Western Ghats. The frog skin was swabbed to determine the presence/absence of Batrachochytrium dendrobatidis, and habitat and environmental characteristics were recorded at sites where W. phrynoderma was found. These data were compared with those of sites apparently lacking this species that had suitable habitat. Walkerana phrynoderma is restricted to evergreen forests between 1300 and 1700 m a.s.l. in the Anamalai Tiger Reserve and at Munnar; thus, its range was extended from the state of Tamil Nadu to the adjoining state of Kerala. Pesticide runoff and human disturbance are the most severe threats to the species; B. dendrobatidis was not detected. This nocturnal anuran prefers forest edges and is associated with well-shaded forest foors in cool areas near freshwater streams. Walkerana phrynoderma is rarely encountered whereas its congener, W. leptodactyla, is more common. The impact of anthropogenic disturbances, especially waste disposal and development of tourism infrastructure, should be evaluated. The land that is owned by the Forest Department peripheral to the protected areas could be designated as eco-sensitive sites to prevent changes in land use that could have an adverse effect on W. phrynoderma.


2005 ◽  
Vol 3 (1) ◽  
pp. 22-25
Author(s):  
YUYUN MARINI ◽  
SUTARNO SUTARNO ◽  
AHMAD DWI SETYAWAN

The aims of the research were: to know species diversity of fern (Pteridophyte) from Pangajaran, Wonosalam, Jombang, to know fern species containing volatile oil, to know concentration and percentage similarity of substances and characteristics of the substances containing in the oil, and to know the structure of cell producing volatile oil in trees and leaf of the fern. Fern diversity was studied by field survey, volatile oil concentration measured by hydro-distillation followed with gas chromatography to further know the components in the oil, while structure of the cell producing volatile oil was detected cross section of the trees and leaf for microscopic analysis. Based on the data and analysis result can be concluded that there were 13 fern species in Pangajaran. Two of the 13 species were confirmed as producing volatile oil, Pteris beaurita Linn. and Cyathea contaminans, that were produced volatile on their leaf only. Concentration of volatile oil of leaf P. beaurita was 0,005%, while in C. contaminans 0,01%. Percentage similarity of the volatile oil between two species based on its Retention Time (RT) was 2,5%, at the RT point of 21.247 in P. beaurita and at RT point of 21.294 in C. contaminans. Percentage similarity of both species based on morphological characters was 36.36%. Location of volatile oil producing cells in both species of fern was spreadly dispersed in schlerenchyma tissue and in mesophyll tissue of the leaf.


Phytotaxa ◽  
2015 ◽  
Vol 231 (3) ◽  
pp. 300
Author(s):  
RAMALINGAM KOTTAIMUTHU ◽  
GUNADAYALAN GNANASEKARAN

During the taxonomic revision of the genus Osbeckia Linnaeus (1753: 345) from the Western Ghats, India, we came across few interesting specimens from the Manjolai hills in Kalakkad Mundanthurai Tiger Reserve (KMTR), Tirunelveli, Tamil Nadu. Critical studies with relevant literature revealed the identity of the collected specimens as Osbeckia tirunelvelica Manickam & Murugan (2001: 626). Unfortunately the name Osbeckia tirunelvelica was not validly published by Manickam & Murugan (2001), because, contrary to Art. 40 of ICN (McNeill et al. 2012), two collections were indicated as “type”. Therefore, the name Osbeckia tirunelvelica is validated here by indicating a single collection as the holotype.


Author(s):  
P. F. Cannon

Abstract A description is provided for Leptogium cochleatum. Some information on its associated organisms and substrata, habitat, dispersal and transmission, and conservation status is given, along with details of its geographical distribution (Africa (Ethiopia, Kenya, Lesotho, Madagascar, Sao Tome and Principe, South Africa, Tanzania), North America (Canada (Nova Scotia), Mexico, USA (Alabama, Arizona, Colorado, Florida, Georgia, Maine, Maryland, Massachusetts, Michigan, Minnesota, New Hampshire, New Jersey, North Carolina, Virginia)), Central America (Belize, Costa Rica, El Salvador, Guatemala, Nicaragua), South America (Argentina, Bolivia, Brazil (Bahia, Mato Grosso, Pará, Rio de Janeiro, Rio Grande do Sul, Santa Catarina, São Paulo), Colombia, Ecuador, French Guina, Peru, Surinam, Venezuela), Asia (China (Beijing, Yunnan), India (Andaman & Nicobar Islands, Karnataka, Maharashtra, Nagaland, Sikkim, Tamil Nadu, Tripura, Uttarakhand, West Bengal), Indonesia, Japan, Malaysia, North Korea, Papua New Guinea, Philippines, Russia (Primorsky Krai), Singapore, South Korea, Taiwan, Thailand, Vietnam), Atlantic Ocean (Bermuda, Cape Verde, Portugal (Azores, Madeira), Spain (Canary Islands), St Helena), Australasia (Australia (New South Wales, Queensland, Victoria), New Zealand, Norfolk Island), Caribbean (Cuba, Guadeloupe), Europe (Austria, Croatia, France, Greece, Ireland, Italy, Norway, Poland, Portugal, Romania, Russia (Krasnodar Krai), Spain, Sweden, Switzerland, UK, former Yugoslavia), Indian Ocean (Mauritius), Pacific Ocean (New Caledonia, USA (Hawaii), Vanuatu)). This species is used in the British Isles as an indicator when making ecological assesments.


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