NOTICEABLE BOOKS ON ORCHIDS OF NEPAL

Nepal being situated at the crossroad of the Himalaya provides a congenial climate for the growth of orchids. The country harbours more than 400 species of wild orchids and has been centre of research. Every year large number of orchid hunters and tourists visit Nepal and get fascinated by this interesting group of plant. However, very few researchers from Nepal are working on orchids and its diversity. Majority of the work are focused on exploration as Nepal is still less explored in terms of flora. In this section, I am trying to compile information on some noticeable books published on orchids from Nepal.
1. Orchids of Nepal by M.L. Banerji. The book was published in 1978 by Bishen Singh Mahendra Pal Singh Publications, Dehradun, India. This book should be the first book published on orchids from Nepal. It contains information on wild orchids (200 orchid species and 54 drawings) collected from Nepal during different expeditions.
2. The Orchids of Nepal Himalaya by ML Banerji and P Pradhan. The book was published in 1984. It contains information on around 250 species with drawings. The publication is based on all the specimens housed in herbaria and botanical surveys.
3. Wild Orchids in Nepal by K White and B Sharma. The book was published in 2000. The book contains information on about 150 species with photographs. This book is based on orchids collected from Tribhuvan Rajpath (highway connecting the capital city of Nepal, Kathmandu and Hetuada) where authors collected orchids during different years.
4. Beautiful Orchids of Nepal by KR Rajbhandari and S Bhattarai. The book is published in 2001 and contains information on 101 species of orchids found wild in Nepal. Information on flowering time, distribution in the world and habitat in Nepal is provided with currently accepted scientific name. The colour photograph of each species is provided such that non-taxonomists can also enjoy beautiful orchids.
5. Nepali Orchids in Pictures by René de Milleville and TB Shrestha. The book is published in 2004 by Malla Prakashan, Kathmandu, Nepal. This book provides information on 140 indigenous species and varieties of orchids in Nepal, including information on the blooming seasons of each and the altitudes and temperatures that they can be found at. While the tables and details may appeal more to botanists and conservationists, the some 250 colour photographs of these beautiful flowers that follow are enough to enchant even the most casual of floral fanciers.
6. The Orchids of Nepal by Bhakta B Raskoti. The book is published in 2009 and provides information on 300+ species with colour photographs. This is the book with information on more than 300 species of orchids from Nepal.
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MEDICINAL ORCHIDS OF NEPAL

Out of more than 400 orchid species in Nepal, 82 species are used for medicinal purpose. An article by me and MB Rokaya contains this information. The article is published on 2010 issue of a journal Our Nature. This article provides information on total number of medicinal orchids (compiled from various published literature) and their distribution pattern in Nepal. Out of 82 species, 33 are terrestrial (40 %), 43 are epiphytic (53 %) and six are of mixed habitat (7 %). The center Nepal harbors highest number of species (69 species i.e.
43%) followed by east Nepal (58 species i.e. 36%) and west Nepal (33 species i.e. 21%). Among them, six species are recorded only from east Nepal, eight species only from center Nepal and three species only form west Nepal and rest of the species are recorded from wider distributional ranges. Maximum richness of total medicinal orchid species richness is observed at an elevation of 1700 m a.s.l.

List of orchids used for medicinal purpose in different parts of Nepal is provided below:

S.N. Accepted name of a species Altitudinal distribution Medicinal use Source/s
1 Acampe praemorsa (Roxb.) Blatt. & McCann 200-1200 Vaidya et al. 2000
2 Aerides multiflora Roxb. 200-1100 Vaidya et al. 2000
3 Aerides odotata Lour. 200-1200 Shrestha 2000, Vaidya et al. 2000
4 Anoectochilus setaceus Blume 1000-1500 Vaidya et al. 2000
5 Arundina graminifolia (D.Don) Hochr 400-2300 Vaidya et al. 2000
6 Brachycorythis obcordata (Lindl.) Sunnerh. 1000-2638 Jha et al. 1996, Shrestha 2000, Vaidya et al. 2000, Rajbhandari 2001, Manandhar 2002, IUCN 2004, DPR 2007
7 Bulbophyllum careyanum (Hook.) Sprengel 6002100 Subedi 2003
8 Bulbophyllum leopardinum (Wall.) Wall. Ex lindl. 1500-3200 Subedi 2003
9 Bulbophyllum umbellatum Lindl. 300-1800 Shrestha 2000
10 Calanthe griffithii Lindl. 2200-2300 Subedi 2003
11 Calanthe plantaginea Lindl. 1500-2200 Subedi 2003
12 Calanthe sylvatica (Thouars) Lindl. 1500-2800 Vaidya et al. 2000, Manandhar 2002
13 Coelogyne corymbosa Lindl. 1500-2900 Shrestha 2000, Vaidya et al. 2000, Manandhar 2002
14 Coelogyne cristata Lindl. 675-2450 Vaidya et al. 2000, Manandhar 2002, DPR 2007
15 Coelogyne flaccida Lindl. 900-1100 Manandhar 2002
16 Coelogyne fuscescens Lindl. 1200-1830 Vaidya et al. 2000
17 Coelogyne nitida (Wall. ex. D. Don) Lindl. 1300-2400 Manandhar 2002
18 Coelogyne ovalis Lindl. 500-2700 Shrestha 2000
19 Coelogyne prolifera Lindl. 1000-2300 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000, Manandhar 2002, Subedi 2003
20 Coelogyne stricta (D. Don) Schltr. 14002135 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000
21 Conchidium muscicola(Lindl.) Rauschert 1500-1800 Shrestha 2000
22 Cymbidium alofolium (L.) Sw. 300-1600 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000, Manandhar 2002
23 Cymbidium devonianum Paxton 1500-1800 Manandhar 2002
24 Cymbidium iridioides D.Don 1500-2800 Vaidya et al. 2000
25 Cymbidium longifolium D.Don 1500-3000 Vaidya et al. 2000, Baral & Khurmi 2006
26 Cypripedium cordigerum D.Don 2800-3800 Manandhar 2002
27 Cypripedium elegans Rchb.f. 2500-4200 Vaidya et al. 2000
28 Cypripedium himalaicum Rolfe 3000-4800 Lama et al. 2001, Manandhar 2002
29 Dactylorhiza hatagirea (D.Don) Soó 2800-3960 Shrestha 2000, Vaidya et al. 2000, Lama et al. 2001, Rajbhandari 2001, Manandhar 2002, IUCN 2004
30 Dendrobium amoenum Wall. ex Lindl. 1100-2900 Vaidya et al. 2000
31 Dendrobium crepidatum Lindl. & Paxton 1200-2400 Subedi 2003
32 Dendrobium densiflorum Lindl. 900-2900 Manandhar 2002
33 Dendrobium fimbriatum Hook. 200-2135 Vaidya et al. 2000
34 Dendrobium longicornu Lindl. 1300-2900 Manandhar 1995, Manandhar 2002
35 Dendrobium monticola P.F.Hunt & Summerh. 1525-2700 Shrestha 2000, Vaidya et al. 2000
36 Dendrobium moschatum (Buch.-Ham.) Sw. 200-1200 Subedi 2003
37 Dendrobium nobile Lindl. 400-1500 Shrestha 2000, Vaidya et al. 2000
38 Dendrobium transparens Wall. ex Lindl. 700-2000 Subedi 2003
39 Ephemerantha macraei (Lindl.) P.F. Hunt & Summerh. 500-2400 Jha et al. 1996, Vaidya et al. 2000, IUCN 2004, DPR 2007
40 Epipactis gigantea Douglas ex Hook 2900-3200 Vaidya et al. 2000
41 Epipactis helleborine (L.) Crantz 1500-3300 Shrestha 2000, Vaidya et al. 2000, Rokaya 2002
42 Epipactis royleana Lindl. 1400-3400 Manandhar 2002
43 Eria spicata (D.Don) Hand.-Mazz. 900-2200 Vaidya et al. 2000
44 Eulophia comestrs Wall. 300 Shrestha 2000
45 Eulophia dabia (D.Don) Hochr. 400-2000 Shrestha 2000, Vaidya et al. 2000, DPR 2007
46 Eulophia spectabilis (Dennst.) Suresh 400-1800 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000
47 Flickingeria fimbriata (Blume) A.D.Hawkes
Sharma 2000
48 Flickingeria macraei (Lindl.) Seidenf.
Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000
49 Gymnadenia conopsea (L.) R. Br. 4300 Rokaya 2002
50 Gymnadenia orchidis Lindl. 1352-4700 Manandhar 1995, Vaidya et al. 2000, Manandhar 2002, Rokaya 2002
51 Habenaria commelinifolia (Roxb.) Wall. ex Lindl. 300-1200 Vaidya et al. 2000
52 Habenaria furcifera Lindl. 150-800 Manandhar 2002
53 Habenaria intermedia D.Don 1800-3300 Shrestha 2000, Manandhar 2002
54 Liparis nervosa (Thunb.) Lindl. 1200-2800 Shrestha 2000
55 Liparis rostrata Rchb.f. 2000-3000 Vaidya et al. 2000
56 Luisia trichorrhiza (Hook.) Blume 1000-1400 Vaidya et al. 2000
57 Luisia tristis (G.Forst.) Hook.f. 300-2300 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000, Manandhar 2002
58 Malaxis acuminata D.Don 450-3050 Shrestha 2000, Vaidya et al. 2000, DPR 2007
59 Malaxis cylindrostachya (Lindl.) Kuntze 2100-3500 Manandhar 2002
60 Malaxis muscifera (Lindl.) Kuntze 2000-4100 DPR 2007
61 Nervilia aragoana Gaudich. 500-1300 Vaidya et al. 2000, DPR 2007
62 Oberonia caulescens Lindl. 1300-2400 Vaidya et al. 2000
63 Orchis latifolia Linn.*
Sharma 2000
64 Otochilus porrectus Lindl. 900-2300 IUCN 2004
65 Papilionanthe teres (Roxb.) Schltr. 200-2100 Manandhar 2002
66 Pholidota articulata Lindl. 570-2285 Vaidya et al. 2000, Manandhar 2002
67 Pholidota imbricata Lindl. 600-2900 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000, Manandhar 2002
68 Platanthera sikkimensis (Hook.f.) Kraenzl. 2600-2900 Shrestha 2000, Vaidya et al. 2000
69 Pleione humilis (Sm.) D.Don 1800-3000 Manandhar 2002
70 Pleione maculata (Lindl.) Lindl. & Paxton 1400-2700 Shrestha 2000, Vaidya et al. 2000
71 Pleione praecox (Sm.) D.Don 1500-2500 Rajbhandari 2001, Manandhar 2002
72 Ponerorchis chusua (D.Don) Soó 2400-4900 Rokaya 2002
73 Rhynchostylis retusa (L.) Blume 300-1850 Shrestha 2000, Vaidya et al. 2000, Manandhar 2002, DPR 2007
74 Satyrium nepalense D.Don 600-4600 Shrestha 2000, Vaidya et al. 2000
75 Smitinandia micrantha (Lindl.) Holttum 500-1400 Vaidya et al. 2000, Rajbhandari 2001, Manandhar 2002
76 Spiranthes sinensis (Pers.) Ames 150-4600 Shrestha 2000, Vaidya et al. 2000 Rokaya 2002
77 Thunia alba (Lindl.) Rchb.f. 500-1800 Manandhar 2002
78 Trudelia praviflora* 350-915 Vaidya et al. 2000
79 Vanda cristata Wall. ex Lindl. 620-2300 Vaidya et al. 2000, Rajbhandari 2001, Manandhar 2002
80 Vanda tessellata (Roxb.) Hook. ex G.Don 200-600 Rajbhandari et al. 2000, Shrestha 2000, Vaidya et al. 2000
81 Vanda testacea (Lindl.) Rchb.f. 460 Vaidya et al. 2000
82 Zeuxine strateumatica (L.) Schltr. 230-1220 Shrestha 2000, Vaidya et al. 2000

Full article can be found here.

FOOD-DECEPTIVE ORCHID SPECIES FLOWER EARLIER AND OCCUR AT LOWER ALTITUDES THAN REWARDING ONES

Food-deceptive pollination is common within the family Orchidaceae in which plants do not offer any food reward reward to their pollinators. As food-deceptive orchids are poorer competitors for pollinator visitation than rewarding orchids, their occurrence in a given habitat may be more constrained than that of rewarding orchids. Study on European orchids by Pellissier et al (2010) found some interesting facts on this. According to them, deceptive orchid species start flowering earlier than rewarding orchids do. Also, the relative frequency of deceptive orchids decreases with altitude, suggesting that deception may be less profitable at high compared to low altitude. Paper based on this findings in published in Journal of Plant Ecology,3(4),243-250. Link for article.

Spiranthes spiralis (L.) Chevall

Photos of Spiranthes spiralis (L.) Chevall collected from Pokhara valley. The species is newly reported from Nepal.

ORCHID SPECIES FIRST TIME REPORTED FROM CENTRAL NEPAL

One species of orchid (Spiranthes spiralis) is first time reported from Pokhara, Central Nepal. Information on this species is published in a reputed journal, Hardvard Papers in Botany, Vol 15(1):71-72, 2010. The article is published by fours authors where i am the first and corresponding author. If you are interested in further information, you can contact me.

TWO NEW ORCHIDACEAE FROM CENTRAL NEPAL

Two new species of orchids: Eria annapurnensis L.R.Shakya & M.R.Shrestha, a new species, and Gastrochilus calceolaris var. biflora L.R.Shakya & M.R.Shrestha, a new variety (both Orchidaceae), are reported from Annapurna Conservation Area, Central Nepal. The article based on these two orchids is published in a journal, EDINBURGH JOURNAL OF BOTANY. Diagrammatic sketch of these two species is presented below:

NEW ORCHID SPECIES RECORDED FROM NEPAL

New species of orchid, Goodyera foliosa (Lindl.) Benth. ex C.B. Clarke var. commelinoides (Fukuy.) F.Maek is for the first time reported from Nepal. The species is first time reported by Bhakta B. Rajkoti and Rita Ale. Article based on this species is published in a journal, Scientific World, Vol. 7(7), 2009. The species is collected from Sundarijal, Shivapuri National Park, Central Nepal at an altitude of 1600 m a.s.l. For details of a species see the journal, Scientific World.

THE ROLE OF CITES IN ORCHID CONSERVATION

Scientists have traced orchids as far back as 120 million years. These plants first received recognition in the herbal writings of Japan and China 3,000 to 4,000 years ago. Once the province of rulers and other powerful officials, orchids are now widely available. The elegant, often brilliantly colored plants grace restaurant tables, offices, homes, and department stores. During the past 10 to 15 years, orchids have achieved unprecedented commercial popularity. They have been the subject of popular books (The Orchid Thief, Orchid Fever) and a movie (Adaptation). In the United States alone, the orchid business exceeds $100 million annually, according to a USDA Floriculture Crops Report.
There are over 20,000 species in the family Orchidaceae, within about 900 genera. The actual number is unknown and the subject of debate, with new species still being discovered. The entire orchid family has been included in the CITES Appendices since the treaty entered into force in 1975. Several species were included in Appendix I because they were over-collected from the wild for horticulture. In 1989, all species in the genera Paphiopedilum and Phragmipedium, the tropical slipper orchids, were transferred to Appendix I because of the high rate of endemism (occurring within a small area) within each genus, the rarity of some species, the similarity of appearance among many species, and their popularity in trade. The vast majority of orchids were included in Appendix II because they resemble other species of conservation concern.
Import and export data indicate that 20 to 25 million or more orchid plants are traded each year worldwide. The overwhelming majority, 95 percent or more, are Appendix-II artificially propagated species and their hybrids, comprising several popular genera. Given these statistics, one might wonder why CITES still protects artificially propagated plants.
When not in flower, some orchids can be indistinguishable from each other, even to a professional. This similarity of appearance facilitates the poaching and subsequent commercial use of wild orchids. For example, tropical slipper orchids have been the subject of intense collection pressure. The recent discovery of a new Phragmipedium species in Peru provides an example. Once news of this magnificently huge-blossomed orchid broke, every plant in the original population was eliminated from its wild environment within a matter of days as collectors ravaged the hillsides where it was found. Orchids continue to be listed under CITES to discourage the poaching of wild plants and to limit opportunities for wild specimens to slip into commercial trade.
For Appendix-II orchids, the CITES Parties decided that trade in certain parts and products is not detrimental to the survival of the species. They agreed to exempt the following from CITES permitting requirements: seeds; pollinia (the encapsulated pollen of orchids); tissue cultures and flasked seedlings; cut flowers of artificially propagated plants; and, for Vanilla species, fruits, parts, and derivatives from artificially propagated plants. Generally, trade in any parts or derivatives of Appendix-I orchids requires a permit, although the CITES Party countries have agreed to exempt flasked seedlings in sterile culture if they meet the CITES definition of artificially propagated plants.
The CITES Plants Committee, which provides technical and scientific support to the Parties, recently reviewed the listing of orchid species to see if it was possible to deregulate certain plants without adversely affecting those that need protection. The goal of this review was to reduce the burden on permit-issuing agencies, border inspection officials, and the regulated public. CITES countries also sought an alternative approach that could focus conservation attention on those species that are removed from the wild each year for international trade.
A comprehensive review of the orchid trade, based on 1995-1999 data, revealed that most of the trade involved 40 genera, which are traded in the thousands. Of the other orchid genera, 326 had never been recorded in trade; 201 had only been traded for scientific purposes; and, for 105, fewer than 50 specimens had been recorded. This analysis suggested that more than half of the known genera of orchids might conceivably be removed from CITES controls.
The Plants Committee concluded, however, that all orchids should remain listed due to the enormity of the orchid family, the difficulty of distinguishing different genera based on vegetative characteristics alone (orchids generally are not traded while flowering), and the confusion that could result from extensive compilations of genera listed and unlisted under CITES. As a consequence, the Plants Committee considered whether some other approach to deregulation might be possible.
In 2001, the Plants Committee asked the U.S. to work with the American Orchid Society to develop a proposal for exempting artificially propagated hybrids of six popular orchid genera--Cattleya, Cymbidium, Dendrobium, Oncidium, Phalaenopsis, and Vanda--from CITES permitting requirements. The rationale for such a proposal was that these genera are traded in high volumes, mostly as hybrids that are generally highly uniform in size and overall appearance. This facilitates their identification as artificially propagated specimens. At their 2002 meeting in Santiago, Chile, the CITES Parties agreed to exempt only artificially propagated Phalaenopsis hybrids as a test case to see if such an approach would be workable. At their most recent meeting, in Bangkok in 2004, the Parties agreed to exempt the artificially propagated hybrids of four Southeast Asian genera: Cymbidium, Dendrobium, Phalaenopsis, and Vanda.
While CITES countries continue to consider whether to deregulate elements of the orchid trade involving little or no conservation risk, it remains a challenge to protect species vulnerable to over-exploitation by the international market. As orchids become increasingly popular, CITES countries continue to work to ensure the protection of wild populations.
Spurce:Endangered Species Bulletin

POLLINATION: SELF-FERTILIZATION STRATEGY IN AN ORCHID

An orchid that flowers in harsh conditions pollinates itself unassisted by any of the usual agents. Mating in flowering plants normally relies on animals, wind, gravity or secretion to convey pollen grains from the male (anther) to the female (stigma) organ1. Apart from that, a new type of self-pollination mechanism in the tree-living orchid Holcoglossum amesianum, is observed in which the bisexual flower turns its anther against gravity through 360° in order to insert pollen into its own stigma cavity — without the aid of any pollinating agent or medium. This mode of self-pollination, which occurs under windless, drought conditions when insects are scarce, adds to the variety of mechanisms that have evolved in angiosperms to ensure their reproductive success.
Almost two thousand H. Amesianum flowers were studied over three flowering seasons in forests in the Yunnan province of China. Each flower has a beak-like projection, known as the rostellum, which separates the anther, the male organ of the flower, from the female stigma cavity. During self-pollination, the anther extends itself downward beyond the rostellum and then thrusts itself upwards to insert pollen into the stigma cavity. All of the flowers were found to use this strategy, and over half succeeded at self-pollination with almost all of these going on to bear fruit.
Source: http://www.nature.com/nchina

ORCHID SPECIES LOSS BY CLIMATE CHANGE

Climate change has led to major changes in the phenology (the timing of seasonal activities, such as flowering) of orchids along with some other species. This result came after the analysis of dataset of the flora of Massachusetts where the informations on life spans of ≈150 years in species abundance and flowering time were observed. Species that do not respond to temperature have decreased greatly in abundance, and include orchids and others like anemones and buttercups, asters and campanulas, bluets, lilies, roses etc. Because flowering-time response traits are shared among closely related species, the findings suggest that climate change has affected and will likely continue to shape the phylogenetically biased pattern of species loss.

Detail of this information can be obtained from PNAS on November 4, 2008 vol. 105 no. 44 17029-17033.

MASSIVE FOREST FIRE IN LANGTANT NATIONAL PARK

News from NASA
On March 12, 2009, the Moderate Resolution Imaging Spectroradiometer (MODIS) on NASA’s Aqua satellite caught a glimpse of a relatively rare event: large–scale forest fires in the Himalaya Mountains of Nepal. Places where the sensor detected active fires are outlined in red. The numerous small fires in southern Nepal may not be wildfires, but rather agricultural or other land-management fires.

The image is centered on Nepal, and it shows the towering Himalaya Mountains arcing through the small country. Many national parks and conservation areas are located along the northern border of the country, and the fires appear to be burning in or very near some of them. Five people were killed by the forest fire southwest of Annapurna in early March; according to a news report they were overtaken while in the forest gathering firewood. According to that report, Nepal commonly experiences some small forest fires each spring, which is the end of the dry season there. However, conditions during the fall and winter of 2008 and 2009 were unusually dry, and fires set by poachers to flush game may have gotten out of control.



Source:www.nasa.gov