ArticlePDF Available

Abstract and Figures

The genus Rhododendron L. (Ericaceae) is represented by about 80 species in India. It is distributed mainly in different regions and altitudes of Himalayas with a greater concentration in the eastern Himalayas. In this paper, the habitat and ecological aspects of rhododendrons in India are presented with particular emphasis on different physical factors. The influences of anthropogenic as well as catastrophic activities, which cause serious depletion of rhododendrons in their natural habitats, are also discussed.
Content may be subject to copyright.
14 WINTER 2008
Debjyoti Bhattacharyya* and M.
Sanjappa
Botanical Survey of India, CGO Complex,
3rd MSO Building, Block F, 5th
Floor, DF Block, Sector I, Salt Lake
City, Kolkata 700 064. West Bengal.
India.
Abstract
e genus Rhododendron L. (Ericaceae)
is represented by about 80 species in India.
It is distributed mainly in different regions
and altitudes of Himalayas with a greater
concentration in the eastern Himalayas.
In this paper, the habitat and ecological
aspects of rhododendrons in India are
presented with particular emphasis on
different physical factors. e influences
of anthropogenic as well as catastrophic
activities, which cause serious depletion of
rhododendrons in their natural habitats,
are also discussed.
Keywords: Rhododendron, India, habitat,
physical factors, threats.
____
Rhododendrons are among the most
popular flowering plants that adorn the
mountains with fantastic and ineffable
flowers of different shades. e rich
variety of rhododendron foliage can equal
the delights of their blooms, especially
the young shoots. Some species are also
very charming for their attractive fragrant
flowers.
It is the largest genus of the family
Ericaceae as well as among one of the largest
flowering plant genera in Asia (Cullen
and Chamberlain, 1978). Globally, the
genus is represented by about 1025 species
(Chamberlain et al., 1996).
e genus is mostly concentrated
in the temperate regions of northern
hemisphere especially in Sino-Himalayas
(Eastern Himalayas and Western China).
Besides this main center,
rhododendrons are further extended
towards southern China as well as to
northeastern China and Japan. About 571
species are found in China (Mingyuan et
al., 2005). A good number are also found in
Myanmar, ailand, Malaysia, Indonesia,
Philippines and New Guinea. 155 species
are endemic in New Guinea (perhaps
a secondary center of distribution).
A few species are also reported from
Afghanistan, Pakistan, southern Europe
and northern America. Two species are
reported from Australia. e most striking
fact is that there are no rhododendrons
in Africa, central and southern America
(Hutchinson, 1947). In India, there are
about 80 species with 10 subspecies and
14 varieties (Bhattacharyya, 2005).
Distribution in India
Rhododendrons of India are widely
distributed in different regions and
altitudes mainly in the Himalayas
(Figure 1). Of the four parallel ranges in
Himalayas, rhododendrons are practically
absent in the Siwaliks, a few are found in
the lesser Himalayas and majority of them
are in the greater Himalayas. Only one
species occurs in Trans-Himalayan region
located in extreme north-west of India
(including the cold deserts of Jammu and
Kashmir and Himachal Pradesh). e
greater Himalayas are thus an ideal locality
for rhododendrons in India. Besides this, a
good number of species are found in north-
eastern India particularly in Naga and
Khasi hills. One subspecies nilagiricum of
Rhododendron arboreum occurs in Western
Ghats.
State-wise, Arunachal Pradesh
harbours the maximum number of
species (67 species) followed by Sikkim
(36 species). 19 species are recognized
from Darjeeling district of West Bengal, 7
from Nagaland, 5 from Manipur, 2 from
Mizoram and Meghalaya each, 6 species
from Uttaranchal and 4 from Himachal
Pradesh and Jammu & Kashmir each.
Only one subspecies is found in Tamil
Nadu and Kerala (Figure 2).
Habitat
e habitat of the genus Rhododendron
ranges from subtropical and temperate
to subalpine and alpine ecosystems. In
India, maximum species diversity (48
species) is recorded from the temperate
and subalpine regions of the Himalayas
between 3000-3500 m (Figure 3). Most
rhododendrons are found in high rainfall,
humid temperate regions of highly organic
well-drained acidic soils and reach their
magnificent development in the high hills
and mountains that have dry, cool summer
and rainy seasons (Milleville, 2002).
Mosses and lichens are commonly
found in association with Rhododendron
species. e epilithic/epiphytic rhododen-
drons grow on the moss-wrapped rocks
and tree trunks associated with Agapetes,
Vaccinium and orchids. Eight species are
found growing epilithically/epiphytically,
which are confined to eastern Himalayas
and north-east India. Such species are
entirely absent in western Himalayas.
Most of the arboreal species are found
in mixed broad-leaved forests in subtropical
regions, sometimes form the dominant
canopy of pure ericaceous forests (Figure
4a) along with Gaultheria. Shrubby
species grow in temperate forests (between
2700-2900 m) and in subalpine regions
(between 2900-3500 m) in association
with Abies, Tsuga, Betula, etc. In western
Himalayas and in eastern Arunachal
Pradesh (Lohit district), rhododendrons
are found associated with chir pine (Pinus
roxburghii). Alpine rhododendron scrubs
(Figure 4b) are found above 3500 m and
Rhododendron Habitats in India
JOURNAL AMERICAN RHODODENDRON SOCIETY 15
Figure 1. Map showing distribution of Rhododendrons in
India.
(Map source National Atlas and Thematic Mapping Organi-
sation, Department of Science & Technology, Government of
India, Kolkata – 700 064; Map outline drawn from India-Phys-
iography, Plate 2).
Figure 2. Species richness of Rhododendrons in different
states in India.
Figure 3. Species richness of Rhododendrons in different al-
titudes in India.
are dominant between 4200-4600 m.
Rhododendron nivale occurs above 5000
m, sometimes near glacier. Many species
are cultivated in the gardens of subtropical
areas.
Factors Responsible for Supporting
Rhododendrons
Soil
Rhododendrons, in general, grow in
well-drained acidic soils, which are rich
in organic matter and low in elements.
Most species grow on slopes where there
is no water logging. Some species like
R. hodgsonii, R. falconeri, etc., are found
in swampy soils and they usually leave
behind fibrous remnants of old leaves on
the ground. Epilithic/epiphytic species
grow either on heavily moist mossy rocks
or pendulous from cliffs (Figure 4c) or tree
trunks. Alpine species like R. anthopogon,
R. lepidotum, R. setosum and R. nivale grow
in soil with limited water and nutrients. In
alpine pastures, all these species are buried
under snow during winter, and when the
snow melts in summer, the soil is exposed
for a period of 3-4 months and the plants
start sprouting (Figure 4d) and flowering.
e soil of the temperate regions are
exposed a little earlier to that of subalpine
and alpine areas and the sprouting starts
at lower elevation and gradually proceeds
upward. e soil of the subtropical
regions of the Himalayas and Western
Ghats remains free from snow, where R.
arboreum grows.
Humidity and Rainfall
According to Indian meteorological
tables (1931-1990), the North-East India
experiences high rainfall (240-1142 cm
per annum) because of its proximity to
Bay of Bengal and direct exposures to
the South-West Monsoon. e Eastern
Himalayas receive 200-500 cm annual
rainfall. It gradually decreases towards
west and becomes minimum (11-75 cm
per annum) in the Trans-Himalayas. e
16 WINTER 2008
Eastern Himalayas receive as much as 100-
200 cm more precipitation per annum
than the Western Himalayas. Annual
average rainfall of one of the collection
localities (Darjeeling district) of different
species of Rhododendron is c. 285 cm. Six
species occur in western Himalayas, where
annual average rainfall is c. 195 cm. e
species like R. anthopogon, R. lepidotum
grow in higher elevations of Jammu and
Kashmir and Himachal Pradesh, where
annual average rainfall is c. 34 mm. R.
nivale occurs at an elevation of more
than 5000 m, where the habitat is totally
dry with incessant cold rain or sleet in
summer. As the weather is very dry in
their habitat, there is an adaptation to
check the transpiration rates by reducing
the leaf surface area. On the other hand,
maximum number of species occurs in
the moist region like north-eastern India.
R. arboreum subsp. nilagiricum grows in
moist areas of Western Ghats particularly
in Ooty, Kodaikanal (Tamil Nadu) and
Munnar (Kerala). In the moist region, tree
species are abundant which form mixed
or pure Rhododendron forest (Figure 4e).
Some species survive in both the moist
and partly dry conditions.
Light
e alpine meadows above 3000 m are
relatively shiny compared to subtropical
Himalayas. e rhododendrons in these
areas have dwarf, stunted habit (Figure 4f).
Duration of light period in Himalayas is
severely affected between 1500-3000 m
due to formation of fog and clouds during
flowering season of rhododendrons (late
March-May). Different rhododendrons in
cloud-affected areas include many broad-
leaved species like R falconeri, R. grande, R.
hodgsonii, R. sinogrande, etc. Some other
species found in association with these
broad-leaved species are R. barbatum, R.
campylocarpum, R. thomsonii, etc., which
are characterized by relatively smaller
leaves. Species occurring in the foggy/
cloudy area (below 3000 m) show broader
and longer leaves than those occurring
above 3000 m.
Exposed hills in north and north-
east are the places of luxuriant growth of
rhododendrons. Flower colour sometimes
may vary with different slopes on which
they grow. Generally, plants with darker
shades of flowers grown in sun-exposed
slopes become pale and faded when grown
in the shade.
Temperature
e effect of temperature on the growth
and flowering of different species of
Rhododendron is directly related as
observed during the course of this study.
A plant of R. arboreum subsp. arboreum
var. arboreum from Lachung (altitude ca
3000 m; temperature recorded was 8°C-
12°C during day, 1°C-3°C during night
in the month of April), North Sikkim
was introduced in the nursery of Indian
Botanic Garden (IBG), Howrah (sea
level) grew to c. 10 cm in 5 years where
the average temperature ranges from 25°-
33°C. Another plant of R. falconeri from
Varsey Rhododendron Sanctuary (2900
m, temperature recorded was 12°C-
15°C during day, 1°C-5°C during night
in the month of April) West Sikkim was
introduced in the Garden of Sikkim
Himalayan Circle (ca 1800 m, average
temperature ranges from 15°C-23°C),
Botanical Survey of India, Gangtak
whose growth rate was also very slow. In
contrast, the other species like R. formosum
(introduced from Elephant falls, upper
Shillong, 1960 m, temperature recorded
during day 12°C-15°C during late March)
is somewhat heat tolerant which flowered
in the gardens of Eastern Circle, Botanical
Survey of India, Shillong (1550 m) where
the average day temperature recorded at
the beginning of April was 19°C-21°C.
R. griffithianum also flowers in slightly
warmer conditions in comparison to other
species.
In alpine zones, the dwarf
rhododendrons remain dormant under
snow during winter seasons to overcome
unfavourable cold period. ough, no
snow is observed in alpine meadows
during flowering seasons (particularly
July) of these species, the temperature
is much less (near 0°C at night). e
alpine rhododendrons adapt themselves
physiologically to withstand the cold
conditions throughout the year. Cox
(1990) reported that the curling of leaves
in cold weather is a natural mechanism,
not only to reduce water loss but also to
shed snow.
Altitude
e habit of the Rhododendron species
is directly related to the altitude of
their habitat. Any tall tree species of
comparatively lower elevations may get
dwarfed when exposed to unfavourable
conditions in higher elevations. Altitude
coupled with other factors like light and
temperature is supposed to be responsible
for the growth patterns of different species.
Cox (1990) stated that high elevations
and wind can make species dwarf, which
normally attain much larger proportions
in lower, more sheltered positions. Species
growing in higher altitudes often have
thicker indumentum than those occurring
in the lower elevations. Moreover, the
thickness of the indumentum sometimes
also varies within the same species growing
in different altitudes. Further, J. D.
Hooker (1854) showed that the duration
between flowering and seed ripening
is directly related to the altitude of the
habitat of a particular species. Generally,
plants at higher elevation take less time for
seed ripening than those at lower altitudes.
According to Kingdon-Ward (1934), the
alternate wetting, drying and freezing day
after day in frosted environment may be
responsible for earlier maturity of seeds.
Slope
Slope is also an important factor,
which has direct bearing on diversity
of species. Some species like R.
falconeri, R. grande, R. hodgsonii, R.
maddenii (when terricolous), R niveum,
etc., prefer to grow in flat ground (Figure
4g) whereas others (R. formosum, R.
johnstoneanum, etc.) like growing in ravines
and on slopes (Figure 4h). is factor is
directly related to the water content of the
soil. As most species prefer well-drained
soils, thus they are slope loving. Maximum
JOURNAL AMERICAN RHODODENDRON SOCIETY 17
species occurs in south facing slopes due to
availability of light and moisture.
Atmospheric Pressure and Velocity of Wind
In alpine zones, low atmospheric pressure
and high velocity of wind cause desiccation
of Rhododendron species, which in turn
modify their growth-form into dwarf
shrubs with stunted or prostrate woody
branches.
Optimal Requirement for Growth and
Flowering of Species
It can be concluded that in general the
physical factors discussed above coupled
with other biological factors have influential
role on the growth pattern and flowering
of different species of Rhododendron. Well-
drained, well-aerated, acidic soil rich in
humus and low in elements, high rainfall,
humid atmosphere, low temperature,
high elevations and sunexposed slopes
are optimal for luxuriant growth of
rhododendrons. Any imbalance in the
ecological factors may cause deterioration
of rhododendron habitat in high
altitudes.
Species Rarity due to Habitat
Destruction
With the diminishing of green cover
almost everywhere, rhododendrons are
also experiencing the impact of disturbed
habitats. Herbarium study and field
observations reveal that many species are
gradually becoming rare. For instance,
entire populations of R. niveum have
almost disappeared and only one patch
of few plants could be traced in the
Yumthang valley, Sikkim during present
study. R. edgeworthii once collected from
Sinchul Lake area, Darjeeling is hardly seen
now. R. vaccinioides could not be located
from the place of its earlier collection in
Fambanghlo Wildlife Sanctuary, Sikkim.
Population coverage of many species like
R. baileyi, R. dalhousieae var. rhabdotum,
R. nuttallii, R. pumilum, etc., are not
considered common species. Rarity
of 14 species is evident from its poor
representation in herbaria. R. maddenii
has also become very rare in its earlier
reported locality (Choongtam) and is now
represented by 1 or 2 plants in isolated
localities along the bank of Lachung Chu
river. Specimens of 7 species were not
found in any Indian herbaria visited during
this study nor could they be collected from
known localities of their earlier collection.
us, out of 80 species in India, 21 can
be considered as rare. However, current
exploration to Arunachal is bringing more
new information regarding the species
richness of the area.
Some of the major causes for rarity of
different species of rhododendrons may
be the changes in climatic conditions of
alpine, subalpine and temperate habitats,
retreating of glaciers, natural disasters like
major landslides and earthquakes. Habitat
destruction due to anthropogenic activities
like logging for firing in construction
of roads (in Tawang and Yumthang),
disposal of waste by tourists and trekkers,
over grazing and over exploitation of
plants for fodder and other purposes are
great potential threats. Jhum cultivation
(shifting cultivation) practiced particularly
in Arunachal Pradesh and Nagaland is
also a major threat for disappearance of
low-altitude species like R. arboreum.
During present study, Saramati mountain
peak, Nagaland (floristically similar to
Japoo hills, which is the Type locality
of many species of Rhododendron) was
visited which is one of the richest areas for
endemic species R. macabeanum. ough
the area was declared as Wildlife Sanctuary
(Fakim WL Sanctuary) but the people
of the nearest village (anamir) totally
depend upon this dominant tree species
of Rhododendron for firewood, which
may cause adverse effect on the entire
population of this species. Leaves and
twigs of R. anthopogon are burnt as dhupi
(incense) in monasteries and temples in
Sikkim, Darjeeling district of West Bengal
and western Arunachal Pradesh (Tawang).
is may lead to large-scale depletion of its
natural population.
Conservation - A Prerequisite
To safeguard the habitats of
rhododendrons from further extinction,
in situ conservation is inevitable. However,
several measures have been taken to protect
the natural habitats of rhododendrons.
e Government has declared many spots
as protected areas in Sikkim (Tiwari and
Chauhan, 2006). Several NGOs are also
engaged in protecting the natural habitat
particularly in Yaksam, West Sikkim. Ex
situ conservation of rhododendrons in
India have also been initiated by G. B.
Pant Institute of Himalayan Environment
and Development at its arboretum near
Pangthang, Sikkim at c. 1800 m altitude
where 24 species are grown (Singh et al.,
2003). Moreover, any effort to check
global warming may secure Rhododendron
habitats from further deterioration.
Acknowledgements
e first author (DB) is thankful to the
Director, Botanical Survey of India for
help and encouragement and for awarding
a Research Fellowship. anks are also
due to the Principal Chief Conservator
of Forest of all the States and Divisional
Forest Officers of all the Protected Areas
visited during the study for issuing research
permit and to forest guards and porters for
their assistance and help during field trips.
References
1. Bhattacharyya, D. 2005. Revision
of the genus Rhododendron L. (Ericaceae) in
India. Ph.D. thesis, University of Calcutta,
Kolkata. (Unpublished).
2. Chamberlain, D. F., R. Hyam,
G. Argent, G. Fairweather, and K. S.
Walter. 1996. e genus Rhododendron:
Its classification & synonymy. Edinburgh:
Royal Botanic Garden.
3. Cox, P. A. 1990. e larger
Rhododendron species. London: B. T.
Batsford Ltd.
4. Cullen, J., and D. F. Chamberlain.
1978. A preliminary synopsis of the genus
Rhododendron. Notes Roy. Bot. Gard.
Edinburgh 36:105-126.
5. Hooker, J. D. 1854. Himalayan
journals. London, Melbourne, New York:
Ward Lock, Bowden Co.
6. Hutchinson, J. 1947. e
Distribution of Rhododendrons. e
18 WINTER 2008
Rhododendron Year Book 1947: 87-98.e
Royal Horticultural Society, London.
7. Kingdon-Ward, F. 1934. A Plant
Hunter in Tibet. London: Jonathan Cape.
8. Milleville, René de. 2002. e
Rhododendrons of Nepal. Nepal: Himal
Books.
9. Mingyuan, F., F. Ruizheng, H.
Mingyou, H. Linzhen, Y. Hanbi, and D.
F. Chamberlain. 2005. Rhododendron in
W. Zhengyi, P. H. Raven and H. Deyuan.
Flora of China 14: 260-455. Beijing:
Science Press and St. Louis: Missouri
Botanical Garden Press.
10. Singh, K. K., S. Kumar, L. K. Rai,
and A. P. Krishna. 2003. Rhododendrons
conservation in the Sikkim Himalaya.
Curr. Sci. 85: 602-606.
11. Tiwari, O. N., and U. K. Chauhan.
2006. Rhododendron conservation in
Sikkim Himalaya. Curr. Sci. 90: 532-541.
*Present address: Institute of Environ-
mental Studies and Wetland Management,
B-4, LA Block, Sector III, Salt Lake City,
Kolkata 700 098. West Bengal. India.
E-mail: dbhatt26@rediffmail.com
Figure 4. Different habitats of rhododendrons. a, Varsey Rhododendron Sanctuary,
West Sikkim, 2900 m – pure broad-leaved rhododendron forest; b, Above Dzongri, West
Sikkim, 4200 m – alpine scrubs dominated by R. anthopogon; c, On way to Chhangu,
East Sikkim, 3100 m epilithic R. camelliiorum hanging from moist cliffs; d, Katao,
North Sikkim, 4100 m – R. lepidotum adapted to survive in snow; e, Above Bikebhanjan,
Darjeeling district, West Bengal, 3100 m dense population of R. arboreum; f, Sela,
Tawang district, Arunachal Pradesh, 4200 m – alpine zone dominated by dwarf, stunted
R. lepidotum (i) and R. anthopogon (ii); g, Valley of Lachung Chu, Choongtam, North
Sikkim, 1830 m R. maddenii in at river bank; h, On way to Elephant falls, above
Shillong, Meghalaya, 1800 m – scattered population of R. formosum in association with
Pinus.
... This is well illustrated from the fact that besides representation by more than 1000 species across the globe (Chamberlain et al., 1996;Fang et al., 2005) it has well established itself in the temperate regions of the Himalayan ecosystem (Fang et al., 2005;Bhattacharya, 2011). Rhododendrons show a wide range of distribution and habitats, covering almost all continents of the world except Africa and Central and South America (Bhattacharya and Sanjappa, 2008). In India, the genus is represented by nearly 87 species 12 sub-species and 8 varieties (Sekar and Srivastav, 2010) with maximum species being reported from Arunachal Pradesh followed by Sikkim (Bhattacharya and Sanjappa, 2008) indicating the North-Eastern dominancy for its occurrence and settlement. ...
... Rhododendrons show a wide range of distribution and habitats, covering almost all continents of the world except Africa and Central and South America (Bhattacharya and Sanjappa, 2008). In India, the genus is represented by nearly 87 species 12 sub-species and 8 varieties (Sekar and Srivastav, 2010) with maximum species being reported from Arunachal Pradesh followed by Sikkim (Bhattacharya and Sanjappa, 2008) indicating the North-Eastern dominancy for its occurrence and settlement. As far as North-Western Himalaya (Uttarakhand in particular) is concerned, the genus is represented by 6 species, Rhododendron arboreum (Sm.), Rhododendron barbatum (Wall.), ...
Article
Full-text available
Rhododendron arboreum (Sm.) is widely known for its multi-purpose use as well as the ecological adaptability it shows encountering different environmental conditions. It is amongst the important taxa of the Indian Himalayan region (IHR). However, being one of the most extensively studied species yet there are many loop areas which are still unexplored particularly for Uttarakhand, India. For instance, there are no records of the number of sub�species and varieties for the genus in the entire Uttarakhand state. Additionally, no emphasis is laid on the study of factors that are responsible for such wide morphological variations in the species. There are no published account highlighting and comparing these variations for entire North-Western Himalayan region. The present paper deals with one such character-the white flowered variant of Rhododendron arboreum (Sm.) which has been not reported from the entire North-western Himalaya region in India, also, it is the first morphological comparative study of both flowers (red and white) of Rhododendron arboreum (Sm.) in India.
... This is well illustrated from the fact that besides representation by more than 1000 species across the globe (Chamberlain et al., 1996;Fang et al., 2005) it has well established itself in the temperate regions of the Himalayan ecosystem (Fang et al., 2005;Bhattacharya, 2011). Rhododendrons show a wide range of distribution and habitats, covering almost all continents of the world except Africa and Central and South America (Bhattacharya and Sanjappa, 2008). In India, the genus is represented by nearly 87 species 12 sub-species and 8 varieties (Sekar and Srivastav, 2010) with maximum species being reported from Arunachal Pradesh followed by Sikkim (Bhattacharya and Sanjappa, 2008) indicating the North-Eastern dominancy for its occurrence and settlement. ...
... Rhododendrons show a wide range of distribution and habitats, covering almost all continents of the world except Africa and Central and South America (Bhattacharya and Sanjappa, 2008). In India, the genus is represented by nearly 87 species 12 sub-species and 8 varieties (Sekar and Srivastav, 2010) with maximum species being reported from Arunachal Pradesh followed by Sikkim (Bhattacharya and Sanjappa, 2008) indicating the North-Eastern dominancy for its occurrence and settlement. As far as North-Western Himalaya (Uttarakhand in particular) is concerned, the genus is represented by 6 species, Rhododendron arboreum (Sm.), Rhododendron barbatum (Wall.), ...
Chapter
Full-text available
Organic mulching is mainly seen as one of the major water saving techniques, because it can slow down the water consumption rate by limiting evaporation losses from both above and below the soil surface and assure the minimal water consumption and also decreased soil erosion in rainy season. However, mulching, especially organic mulching has the ability to enhance the soil's physical characteristics, chemical environment and biological activity.
... R. campanulatum (Ericaceae) is a perennial woody, evergreen large shrub (Schickhoff, 2005) or sub-tree (Singh, 2018), and usually forms a fairly gregarious krummholz on wet slopes at an elevation of 2800 -4400 m in the study area (western Himalaya to western Tibetan region). It prefers organic-rich, well-drained acidic soils, dry, cool summers, and long winters in high rainfall, humid temperate regions (de Milleville, 2002;Bhattacharyya and Sanjappa, 2008). While, B. utilis (Betulaceae) is a long-lived, broadleaved winter deciduous tree that can reach a height of 20 m, it forms fairly extensive canopies at elevations ranging from 2700 to 4500 m (Polunin and Stainton, 1984) and is more abundant between 3048 and 4300 m (Troup, 1921). ...
... This indicates that environmental conditions at middle latitudes in the western Himalayas are more suitable for these species as the seasonal temperature amplitude decreases towards the eastern Himalayas . Bhattacharyya and Sanjappa (2008) claimed that the high concentration of alpine Rhododendron habitat is governed Fig. 6. Factor maps and Biplots of B. utilis and R. campanulatum for BCM, PhenoM, BiophyM and HM (left to right) with common attributes on axis 1 and axis 2. First row (factor maps): the contribution of the environmental variables on axes 1 and 2 of PCA, and the percentage of variation described by axes 1 and 2. Second row (biplots): The different coloured concentration ellipses portray the observations that are grouped as per similar behaviour of environmental spaces for focal species, and the size of the ellipsoid is determined at a 95% probability level. ...
Article
Topical advances in earth observation have enabled spatially explicit mapping of species' fundamental niche limits that can be used for nature conservation and management applications. This study investigates the possibility of applying functional variables of ecosystem retrieved from Moderate Resolution Imaging Spectroradiometer (MODIS) onboard sensor data to map the species distribution of two alpine treeline species, namely Betula utilis D.Don and Rhododendron campanulatum D.Don over the Himalayan biodiversity hotspot. In this study, we have developed forty-nine Novel Earth Observation Variables (NEOVs) from MODIS products, an asset to the present investigation. To determine the effectiveness and ecological significance of NEOVs combinations, we built and compared four different models, namely, a bioclimatic model (BCM) with bioclimatic predictor variables, a phenology model (PhenoM) with earth observation derived phenological predictor variables, a biophysical model (BiophyM) with earth observation derived biophysical predictor variables, and a hybrid model (HM) with a combination of selected predictor variables from BCM, PhenoM, and BiophyM. All models utilized topographical variables by default. Models that include NEOVs were competitive for focal species, and models without NEOVs had considerably poor model performance and explanatory strength. To ascertain the accurate predictions, we assessed the congruence of predictions by pairwise comparisons of their performance. Among the three machine learning algorithms tested (artificial neural networks, generalised boosting model, and maximum entropy), maximum entropy produced the most promising predictions for BCM, PhenoM, BiophyM, and HM. Area under curve (AUC) and true skill statistic (TSS) scores for the BCM, PhenoM, BiophyM, and HM models derived from maximum entropy were AUC ≥0.9 and TSS ≥0.6 for the focal species. The overall investigation revealed the competency of NEOVs in the accurate prediction of species' fundamental niches, but conventional bioclimatic variables were unable to achieve such a level of precision. A principal component analysis of environmental spaces disclosed that niches of focal species substantially overlapped each other. We demonstrate that the use of satellite onboard sensors’ biotic and abiotic variables with species occurrence data can provide precision and resolution for species distribution mapping at a scale that is relevant ecologically and at the operational scale of most conservation and management actions.
... Flowers are used in diarrohea and dysentery Khare (2007) Juice from flowers is very common and a pleasant drink medicinal). Rhododendron sp. have been reported to capable conserve the water moisture at large amount in hill area maintains transpiration rate and humidity in regions with low rainfalls at higher altitudes Chauhan et al. (2017), Bhattacharaya and Sanjappa (2008) controls wind velocity, maintains slope of mountains Bhattacharaya and Sanjappa (2008) and are also beneficial in erosion control Chauhan et al. (2017) The human race does not understand the threat, created by them for survival of this species. Their intrusion in the Himalayan region has reduced the natural population of the species. ...
... Flowers are used in diarrohea and dysentery Khare (2007) Juice from flowers is very common and a pleasant drink medicinal). Rhododendron sp. have been reported to capable conserve the water moisture at large amount in hill area maintains transpiration rate and humidity in regions with low rainfalls at higher altitudes Chauhan et al. (2017), Bhattacharaya and Sanjappa (2008) controls wind velocity, maintains slope of mountains Bhattacharaya and Sanjappa (2008) and are also beneficial in erosion control Chauhan et al. (2017) The human race does not understand the threat, created by them for survival of this species. Their intrusion in the Himalayan region has reduced the natural population of the species. ...
Article
Full-text available
The variety in biodiversity is a boon to human civilization by Mother Nature. Every aspect of this biodiversity from unicellular organisms to multicellular plants are important. India subcontinent being a land of diversity, has a rich resource of flora and fauna. The richness is also contributed by arising of great Himalayan Mountains. In this study, we are presenting a case where increasing human interference is effecting growth and development of a significant species called Rhododendron arboretum. The plant parts of Rhododendron arboretum is useful to mankind medicinally which is very well depicted in ancient and recent literatures.
... Of these, Arunachal Pradesh has the highest number of taxa with 119 (74 species, 21 subspecies, and 24 varieties), followed by Sikkim with 42 taxa (25 species, 11 sub-species, and six varieties), Manipur with 10 taxa, 4 taxa in Mizoram and 11 taxa in Nagaland respectively. One species is found in south India R. nilagiricum (Bhattacharyya and Sanjappa, 2008). The flower has significant ecological and economic importance. ...
... ex D.Don (Myricaceae) in these tehsils. The local populace largely depends on the products of these plants for their personal use as well as for trade purposes (Bhattacharyya and Sanjappa, 2008;Kumar et al., 2019). In view of this, an attempt has been made to assess these two valuable plant species. ...
Article
Full-text available
Inhabitants of the hilly regions largely depend on wild herbs for medicine and food supplements. The indigenous knowledge and traditional use of these wild herbs are vanishing fast. Chachiot and Thunag Tehsils of Mandi District are rich repositories of wild medicinal herbs. Among them includes Rhododendron arboretum Sm. and Myrica esculenta. They have been long used for medicinal and edible purposes. Moreover, their flowers, fruits and other value-added products are sold in the domestic market by the local people. This study aimed to investigate nutritional, and medicinal and to access market demand for the socio-economic development of rural people of the study area. Local inhabitants of Chachiot and Thunag collect their flowers and fruits seasonally from March to May. These are good sources of food, medicine and income for local people.
... Of these, Arunachal Pradesh has the highest number of taxa with 119 (74 species, 21 subspecies, and 24 varieties), followed by Sikkim with 42 taxa (25 species, 11 sub-species, and six varieties), Manipur with 10 taxa, 4 taxa in Mizoram and 11 taxa in Nagaland respectively. One species is found in south India R. nilagiricum (Bhattacharyya and Sanjappa, 2008). The flower has significant ecological and economic importance. ...
Book
Full-text available
... Rhododendron is the largest genus of the family Ericaceae, represented by about 1025 species worldwide and 80 in India, and the genus is mainly distributed from temperate to alpine regions of Himalaya (Bhattacharyya & Sanjappa, 2008). R. arboreum is an evergreen tree with a shallow root-system and is distributed from temperate to alpine regions of Himalaya; the species possess red-coloured scanty flower between March and June (Srivastava, 2012). ...
Article
Full-text available
Flowering exhibits a significant relationship with environmental stimuli and changes. Effect of photoperiodism and vernalization have been well studied in flowering phenology; however, the effect of soil temperature on flowering is less explored which is one of the major factors of vegetation growth in alpine ecosystem. This study thus focuses on the effects of soil and air temperature on flowering response of Rhododendron arboreum Sm., a Himalayan tree species, which is also an indicator of spring initiation in high altitude regions. To monitor the flowering pattern, we employed automated phenocam, which was set up at 3356 masl in Tungnath (Indian Alpine region of Uttarakhand) for time-lapse photography of timberline ecotone. Soil and air temperature were recorded continuously at the timberline ecotone. Three years (2017 to 2020) of datasets were used for the present study. The phenocam observations displayed an interesting event in the year 2019–2020 with complete absence of flowering in R. arboreum population at Tungnath timberline ecotone. From the soil temperature data, an increase in winter (Dec–Jan, during which floral buds form) soil temperature, by > 1 °C, and no accumulation of freezing degree-days were found for the year 2019–2020. Air temperature however did not display any relationship with the failure of flowering, ruling out aerial chilling or frost injury of floral buds. From the results, a possible relationship between soil temperature and flowering can be suggested pointing towards necessary root apex vernalization stimulus in shallow rooted Rhododendrons. However, the dependency of flowering in Rhododendrons on winter soil temperature further requires continuous monitoring and more observations to make concrete inferences.
Article
Full-text available
Rhododendrons form a major plant group at upper temperate locations having a characteristic slow growth rate and sizable horticultural value. Asia is the homeland for rhododendrons and many species had been hunted out of the region during British rule. About 98% of the Indian species are found in the Himalayan region, among which 72% are found in Sikkim. Due to human interference the natural populations of rhododendrons in the entire Himalaya are gradually diminishing. The major threats to rhododendrons are deforestation and unsustainable extraction for firewood and incense by local people. A set of rhododendrons which are classified as rare/endangered may be wiped out from the biota in the near future if proper conservation measures are not made. The present work incorporates biotechnological and conventional methods to counter the threat on survival of these plants. Studies on in vitro Rhododendron maddeni from the cotyledonary nodal segments, young leaves and stems, have yielded positive results. The goal of the work is to find out means of conservation through in vitro and ex situ mass propagation and restoration of rhododendron population in the wild.
Article
A review on the rhododendron conservation effort in the Sikkim and other parts of Indian Himalaya is presented here, with particular emphasis on ecology, baseline assessment, uses, growth studies, ex situ and in situ conservation initiatives. Identification of major gaps and constraints of forestry policy and plans and current practices of rhododendron conservation and management have been made. The impact of land use and management on the conservation of diversity is analysed and discussed. Species richness and diversity are significantly lower in heavily utilized forest. This study emphasizes that the forest rhododendrons in the habitats are severely threatened. Deforestation is the consequence of the tourist pressure for fuelwood along with other reasons in Himalaya. The degradation of rhododendrons in Himalaya is also due to lack of appropriate policy to guide the legal, institutional and operational development for the conservation. There is a need to implement the conservation obligations by transforming them into regulations in order to make them legally binding.
Article
by Joseph Dalton Hooker. "In two volumes." Includes index.
Revision of the genus Rhododendron L. (Ericaceae) in
  • D Bhattacharyya
Bhattacharyya, D. 2005. Revision of the genus Rhododendron L. (Ericaceae) in
The genus Rhododendron: Its classification & synonymy. Edinburgh: Royal Botanic Garden
  • Walter
Walter. 1996. The genus Rhododendron: Its classification & synonymy. Edinburgh: Royal Botanic Garden.
Himalayan journals The Distribution of Rhododendrons. The Rhododendron Year Book
  • J D Hooker
  • J Hutchinson
Hooker, J. D. 1854. Himalayan journals. London, Melbourne, New York: Ward Lock, Bowden Co. 6. Hutchinson, J. 1947. The Distribution of Rhododendrons. The Rhododendron Year Book 1947: 87-98. The Royal Horticultural Society, London.
  • F Chamberlain
F. Chamberlain. 2005. Rhododendron in W. Zhengyi, P. H. Raven and H. Deyuan. Flora of China 14: 260-455. Beijing: Science Press and St. Louis: Missouri Botanical Garden Press. 10. Singh, K. K., S. Kumar, L. K. Rai, and A. P. Krishna. 2003. Rhododendrons conservation in the Sikkim Himalaya.
The Distribution of Rhododendrons. The Rhododendron Year Book
  • J Hutchinson
Hutchinson, J. 1947. The Distribution of Rhododendrons. The Rhododendron Year Book 1947: 87-98. The Royal Horticultural Society, London.