Upload
others
View
2
Download
0
Embed Size (px)
Citation preview
~ 320 ~
Journal of Entomology and Zoology Studies 2018; 6(3): 320-329
E-ISSN: 2320-7078
P-ISSN: 2349-6800
JEZS 2018; 6(3): 320-329
© 2018 JEZS
Received: 17-03-2018
Accepted: 18-04-2018
N Narmadha
PSG College of Arts and Science,
Coimbatore, Tamil Nadu, India
Dr. K Varunprasath
Assistant Professor, M.Sc,
M.Phil, Ph.D PSG College of
Arts and Science, Coimbatore,
Tamil Nadu, India
Correspondence
Dr. K Varunprasath
Assistant Professor, M.Sc,
M.Phil, Ph.D PSG College of
Arts and Science, Coimbatore,
Tamil Nadu, India
Status of butterfly species in Pallassena village,
Palakkad district, Kerala
N Narmadha and Dr. K Varunprasath
Abstract Butterflies are one of the most important assemblages of insects that act as biodiversity indicators as well
as nature’s gardeners. The current survey was carried out to document the butterfly species diversity
along with abundance in Pallassana Village, Palakkad district, Kerala from September 2017 to January
2018. A total of 303 individuals with 57 varieties, under five families of butterflies were recorded.
Among the families, Nymphalidae consist of 27 species followed by Pieridae 12 species, Papilionidae 10
species, Lycanidae 7 species and one Hesperiidae species were observed. Among these families
maximum abundance in Herbs and shrubs habitat with 29 species followed by grassland includes 17
species, agricultural with 9 species. Based on the IUCN list, 26 common species, 16 very common, 12
uncommon species and one rare species were recorded. According to monthly wise abundance,
maximum of 80 species in the month of January where as 4 species in September were observed during
the study.
Keywords: Butterflies, abundance, distribution, diversity indices, Pallassana village
1. Introduction Butterflies are day flyer and a colourful insect belonging to the Order Lepidoptera. These
insects plays an important role in ecosystem as plant pollinator in food chain as herbivores [1].
18, 000 butterfly species around the world. Butterflies respond to trouble and alter in habitat
and act as an environmental pointer [2]. Environmental variations and changes in the forest
composition are severely affected for butterflies because butterflies are directly dependent on
flora [3-4]. Migration or local extinction of butterflies purely based on minor changes in habitat
alteration [4-6]. Butterfly diversity might be reflecting the overall floral variety in the certain
region because of their floral association [7]. Butterflies mixture ultimately reflects overall
plant range specially herbs and shrubs in the region [8].
More than half of the world’s known animal species are insects [9] in which Lepidoptera is the
second largest and the most diverse order in the class Insecta [10]. [11] Documented 19238
species of butterflies in the world. Later, [12] reported 1504 species in Indian subcontinent. [13]
Reported about 177 species of butterflies in Central Provinces [14]. Recorded a total of 167
species of 90 genera from Vidarbha region. In India, out of 1,501 butterfly varieties, 521
Brush-footed butterflies, 443 Blues, 321 are Skippers, 109 Whites and Yellows and 107
Swallowtails [15]. Butterfly species are firmly seasonal and favour only a particular set of
habitats [16]. Butterflies are fine indicators in terms of anthropogenic interruption and habitat
excellence [17]. Out of 18,000 known butterfly species of world, in Indian subcontinent alone
identified around 1500 butterfly species which contain 8.33% [18-19]. In India, during 19th
century the pioneering work in butterfly studies started [12]. 330 butterfly species present in
Western Ghats and 48 species are endemic to Nilgiri Biosphere Reserve (NBR). Out of 1,501
species of butterflies in India, 334 varieties were reported from the Western Ghats and 37
species are endemic to the Western Ghats [20-21]. In Western Ghats has 334 varieties of
butterflies and 316 species reported from Kerala [22]. In Kerala state the documentation of
butterfly species done by several researchers [23-29].
The Western Ghats of India is under threat due to deforestation and one of the hotspots regions [30]. Biodiversity mostly affected by habitat destruction and deterioration feature [31]. Increased
city quality along with road and rail network, buildings leads correspond with decreases in
butterfly species richness, variety and abundance [32-35]. Habitat degradation as well as
decreased floral species diversity, reduced water quality and increased air and soil pollutions
due to urbanization development [36-40]. Use of heavy machinery and increased input of
~ 321 ~
Journal of Entomology and Zoology Studies
insecticides, pesticides and herbicides [41] of these, chemical
pesticides potentially affect development of butterfly larva
and nectar producing plants which adversely affect adult
butterfly diversity. Developments of agriculture field in forest
ecosystem endanger many species throughout the world [42].
2. Materials and Methods
2.1 Study Area
Fig 1: Showing the Satellite map of Pallassana village, Palakkad district, Kerala (Scale-100 feet, 50 meter)
Kerala, traditionally identified as Keralam, is an Indian state
in South India. Palakkad is one of 14 districts of the state of
Kerala in Southern India. Palakkad has a dry climate with the
moderate temperature exception in March and April and
annual rainfall is around 83 inches (211 cm). The summers
are much rainier than the winters in Palakkad. The average
annual temperature in Palakkad is 27.8 °C. In a year, the
average rainfall is 2135 mm. Plains, Mountains, Backwaters,
Forests, Farm lands and including Parambikulam Wildlife
Sanctuary and Silent Valley National Park make up the
topography of the district. In Silent Valley National Park, 128
butterfly varieties and 400 species of moths found inside the
national park under situated this district. In Parambikulam
Wildlife Sanctuary, 39 species of mammals, 280 species of
birds, 61 species of reptiles, 47 species of fishes and
enumerable number of butterflies and insects are sharing this
eco system. Pallassana Village present in Nemmara Block in
Palakkad District and belongs to Central Kerala Division. In
this village, the temperature remains moderate throughout the
year, the annual rainfall around 2,135 millimetres and receive
South-West Monsoon. The forest covers an area of 13, 6,257
hectare which is 25% of the total geographical area, mainly
over the north eastern of the district. The village has a
Gardens, Trees as well as Wild plants. The major Garden
plants are Ixora (Ixora alversia), Hibiscus (Hibiscus syricua),
Catharanthus roses etc. Trees include Palms, Coconut (Cocos
nucifera), Mango trees (Manifera indica) and Jack fruit trees.
2.2 Methodology
The survey was carried out from September 2017 to January
2018 (morning 6.00 am till 7.00 p.m) Pallassana Village,
Palakkad district. The survey of butterflies was undertaken
along five different transects. The butterflies were recorded
using standard transect counting method [43], counted while
walking along the selected transect route of 1 km, in each
habitat. The nomenclature used in the check list of Butterflies
in IUCN (2015) was followed. The transects surveyed of
existing Garden, Agriculture area, Shrubs and herbs,
Grassland areas. Typical and unique features of the wings,
abdomen and pattern of coloration of all body parts were
noted down. Sketches were made accordingly using pencils
and marked the pattern of colour patches and print
distribution. Butterflies were photographed by (Sony W520)
camera, from different angles to enable positive identification
of species. Descriptions, photographs and drawings were
compared with literature and the species were identified based
on the collected data and available reference, both printed and
electronic. Identification of species was confirmed with the
help of the field guides [21] taxonomy and nomenclature has
been updated. Vegetations of each site and sub site were
keenly observed and relevant data were recorded
2.3 Measurement of Diversity
Relative dominance index of the butterfly species was
calculated by
Dominance index (%) = Number of individuals of one species
(n) X 100/Number of individuals of all species (N).
Simpson’s Index is a measure of diversity; it takes into
account the number of species present, as well as the
abundance of each species.
D = Σn (n-1)/ N (N-1)
Where, D-Simpson’s index
n-The number of individuals of each different species
N-The total number of individuals of all species.
Shannon Weaver index is used to characterize species
diversity and abundance in a community. Shannon-Wiener
index (H’) is given as follows
H’= - Σ Pi ln (Pi),
Where, H’-the Shannon’s index, Pi-the proportion of
individuals in the i th species, ln-natural log.
~ 322 ~
Journal of Entomology and Zoology Studies
3. Result
3.1 Table Showing the Status of Butterflies in Pallassena Village, Palakkad District, Kerala.
Common name Scientific name Habitat and host plant
Family name-Nymphalidae
Glassy blue tiger* Parantica aglea GI, Calotropis sp. Ceropegia sp. Cryptolepis buchanani, Tylophora indica, T. tenuis
Lemon pansy* Junonia lemonias GIII, Barleria spp, Hygrophila auriculata, Justicia neesii, J. procumbens, Arrowleaf
Sida Sida rhombifolia, Corchorus capsularis.
Striped tiger* Danus genita GIII, Asclepias currassavica, Ceropegia sp. Cynanchum sp., Marsdenia roylei,
Stepahnotis sp. Tylophora tenuis.
Tawny coster* Acraea tersicore GIII, Adenia hondala, Modecca palmata, Passiflora edulis, P. foetida, P. subpeltata,
Hybanthus enneaspermus, Turnera ulmifolia.
Plain tiger* Danus chrysippus GIII,Calotropis gigantea, C. procera, Cynanchum sp., Frerea indica, Tylophora sp,
Ficus racemosa etc.
Chocolate pansy** Junonia iphita GIII, Carvia callosa (Syn. Strobilanthes callosa), Hygrophila auriculata, Justicia neesii,
Lepidagathis prostrata.
Blue tiger** Tirumala limnaceae GII, Asclepias currassavica, Calotropis procera, Heterostemma sp., Hoya viridiflora,
Tylophora indica, Wattakaka volubilis
Yellow pansy** Junonia hierta GIII, Barleria spp. (B. cristata), Hygrophila auriculata, Bell Weed Ruellia prostrata.
Common evening brown** Melanitis leda GII, Grass spp. including rice (Oryza sativa), bamboo, Imperata, Eleusine spp., and
millets such as Oplismenus compositus, Panicum spp.
Dark evening brown*** Melanitis phedima GIII, Microstegium ciliatum, Setaria palmifolia.
Great evening brown*** Melanitis zitenus GIII, Data deficient.
Common bush brown* Mycalesia perseus GIII, Rice sps.
Dark banded bush brown* Mycalesia mineus GIII, Oryza spp. and grass spp.
Common baron* Euthalia aconthae GIII, Cashew tree Anacardium occidentale, Mango Mangifera indica, Bryonia spp.
Streblus asper.
Joker*** Byblia ilithiya GII, Indian Stinging Nettle Tragia involvucrata, T. plukenetii.
Danaid egg fly* Hypolimnas misippus GIII, Common Purslane Portulaca oleracea, Asystasia lawiana.
Great egg fly* Hypolimnas bolina GII, Abutilon sp. Hibiscus sp. Arrowleaf Sida Sida rhombifolia, Common Purslane
Portulaca oleracea, Elatostemma cuneatum.
Blue pansy* Junonia orithiya GII, Hygrophila auriculata, Justicia procumbens, Lepidagathis prostrata, Nelsonia
campestris, Shame plant Mimosa pudica.
Dark blue tiger** Tirumala septentrionis GI, Vallaris dichotoma, V. heyneii, Cosmostigma racemosa, and Wattakaka volubilis.
Common four ring** Ypthima huebneri GIII, Axonopus compressus, Grass spp.
Common castor*** Ariande merione GIII, Ricinus communis, Indian Stinging Nettle Tragia involvucrata, T. plukeneti.
Commnon crow** Euploea core GI, Nerium indicum, Calotropis gigantea, Hemidesmus indicus, Tylophora indica, Ficus
sp., Streblus asper, Figs.
Common sailor* Neptis hylas GIII, Dalbergia sp. Pongamia glabra, Xylia dolabriformis, Bombax malabaricum,
Thespesia populnea, Zizyphus sp.
Short banded sailor*** Phaedyma columella GIII, Dalbergia spp., Pterocarpus sp.
Common palm fly* Elymnias hypermnestra GIII, Cocos nucifera, Calamus pseudo tenius, Calamus rotang, Calamus thwaitesii.
Niligiri blue tiger*** Parantica niligirensis GI, Tylophora tenuis and T. indica.
Anomalous nawab* Polura agrarian GIII, Data deficient.
Family name-Papilionidae
Crimson rose* Atrophaneura hector GI, Aristolochia indica, A. bracteolata, and Thottea siliquosa.
Common mormon** Papilio polytes GI, Aristolochia bracteolate, A. indica, A. tagala, A. griffithi, A. elegans, Thottea
siliquosa.
Common mormon** Papilio Romulus GI, Aristolochia bracteolate, A. indica, A. tagala, A. griffithi, A. elegans, Thottea
siliquosa.
Common mormon** Papilio stichius GIII, Aristolochia bracteolate, A. indica, A. tagala, A. griffithi, A. elegans, Thottea
siliquosa.
Common jay*** Graphium doson GII, Cinnamomum macrocarpum, Magnolia grandiflora, Michelia champaca, Milliusa
tomentosum and Polyalthia longifolia.
Tailed jay*** Graphium Agamemnon GI, Lime, orange and lemons. C. aurantifolia, C. sinensis, Atalanta racemosa, Glycosmis
arborea, Curry Tree Murraya koenigii.
Lime butterfly** Papilio demoleus GIII, Glycosmis pentaphylla, Cultivated lime, C. grandis, orange and lemons. C.
Aurantifolia, C. sinensis, Atalanta racemosa, C. limo.
Blue mormon* Papilio polymnestor GII, Glycosmis arborea, and Citrus grandis, Atalantia wightii, Paramigyna monophylla,
Citrus limon. Atalantia racemosa.
Common rose** Atrophaneura
dristolochiae
GII, Aristolochia bracteolate, A. indica, A. tagala, A. griffithi, A. elegans, Thottea
siliquosa.
Citrus swallow tail*** Papilio demoleus GIII, Anacardiaceae,Apiaceae,Rutacea,Sapindaceae,
Family name-Pieridae
Mottled emigrant** Catopsilia pyranthe GII, Cassia spp. (e.g. C. fistula, C. auriculata, C. occidentalis, C. tora), Sesbania
bispinosa.
Common emigrant** Catopsilia Pomona GII, Species of Cassia. Other host plants include Palash or Flame of the Forest Butea
monosperma, Cassia fistula.
Small grass yellow * Eurema brigitta GII, Cassia cleinii, Smithia sensitiva, Chamaecrista mimosoides.
Common grass yellow* Eurema hecaba GII, Abrus precatorius, Aeschynomene spp. (A. americana, A. indica), Calliandra
~ 323 ~
Journal of Entomology and Zoology Studies
haematocephala, Senna alata.
Common jezebel* Delias eucharis GI, Dendrophthoe falcata, Helicanthes elastica, Scurrula parasitica, Viscum spp.
Cabbage butterfly* Pieris rapae GIII, Nasturtium spp., Rorippa dubia, Sisymbrium sp., Cabbage and related species.
Psyche** Leptosia nina GIII, Cleome viscosa, Capers e.g. Capparis zeylanica, C. rheedii, C. sepiaria, C.
spinosa, Crataeva adansonii.
Common wanderer* Pareronia valeria GIII, Capparis heyneana.
Crimson tip* Colotis danae GII, Capparidaceae,the Indian caper,Capparis divaricata,Macruna oblongifolia,
Cadaba fructicosa.
Lemon emigrant** Catopsilia crocale GIII, ndian laburnum, Kassod tree, Flame of the forest,Bauhinia racemosa.
Family name-Lycaenidae
Common cerulean* Jamides celeno GII, Saraca asoka, Abrus precatorius, Butea monosperma, Phaseolus adenanthus,
Pongamia pinnata, Xylia xylocarpa.
Samll cupid*** Chilades parrhasius GIII, Bell Mimosa Dichrostachys cinerea.
Common silver line*** Spindasis vulcanus GII, Jamides celeno
Forgot me not* Catochrysops Strabo GII, Ougeinia dalbergioides, Cylista scariosa, Desmodium elegans, cultivated legumes,
Schleichera trijuga.
Common pierrot* Castalius rosimon GIII, Ziziphus jujuba, Z. mauritiana, Z. rugosa.
Malayan* Megisba Malaya GIII, Allophyllus cobbe, Kumkum tree Mallotus philippensis.
Pea blue**** Lampides boeticus GIII, Fabacea species like Medicago, Crotalaria, Polygala, Dolichus, Cytisus.
Family name-Hesperiidae
Samall branded swift*** Pelopidas mathias GII Axonopus compressus, Grass spp.
Common*, Very common**, Uncommon ***, Rare ****
Group I (GI)-Agriculture field, Group II (GII)-Grassland, Group III (GIII)-Herbs & shrubs
The family-wise composition of butterfly species at Palakkad
district was recorded. Fifty five butterfly varieties under five
families including three different habitats surveyed. Famliy
Nymphalidae with maximum of (n=27) species consist of
49%, including Parantica aglea, Junonia lemonias, Danus
genita, Acraea tersicore, Danus chrysippus,Junonia iphita,
Tirumala limnaceae, Junonia hierta, Melanitis leda, Melanitis
phedima, Melanitis zitenus, Mycalesia perseus, Mycalesia
mineus, Euthalia aconthae, Byblia ilithiya, Hypolimnas
misippus, Hypolimnas bolina, Junonia orithiya, Tirumala
septentrionis, Ypthima huebneri, Ariande merione, Euploea
core,Neptis hylas, Phaedyma columella, Elymnias
hypermnestra, Parantica niligirensis, Polura agrarian
followed by Papilionidae with (n=10) species consist of
18.1% of butterflies(Atrophaneura hector, Papilio polytes,
Papilio Romulus, Papilio stichius, Graphium doson,
Graghium Agamemnon, Papilio demoleus, Papilio
polymnestor, Atrophaneura dristolochiae, Papilio demoleus),
family Pieridae with (n=10) species consist of 18.1%
(Catopsilia pyranthe, Catopsilia Pomona, Eurema brigitta,
Eurema hecaba, Delias eucharis, Pieris rapae, Leptosia nina,
Pareronia valeria, Colotis danae, Catopsilia crocale),
Lycaenidae with (n= 7) species consist of 12.7% including
Jamides celeno, Chilades parrhasius, Spindasis vulcanus,
Catochrysops Strabo, Castalius rosimon, Megisba Malaya,
Lampides boeticus and found to be minimum in Hesperidae
with (n=1) species consist of 2% of Pelopidas mathias were
recorded.
Table 2: Diversity Indices of Butterfly Species in Five Different Habitats
Habitat Shannon index Simpson index Dominance Index Margalef index Pielouf index
Agricultural field 0.964 2.455 16.363 56.589 0.5544
Grassland 1.498 4.188 30.909 43.886 0.8611
Shrubs& Herbs 1.077 2.304 52.727 36.925 0.6189
The values of Pielouf’s index indicate that there is an equal
distribution of the species in all five different habitats and
even with high value in Grassland habitat with (0.8611)
Agricultural field and shrubs habitat shows the lowest value
of Pielouf index ranges from (0.5544 to 0.6189) and it is not
possible to identify a dominant habitat ranges. In Grassland
habitat the Shannon index value was the highest represents
(1.498) and lowest in Argicultural field with (0.964). The
Grassland habitat shows the highest value of Simpson index
with (4.188) and lowest value was found to be in Shrubs and
herbs habitat with (2.304). Margalef index presents high value
in Agricultural field presenting (56.589) and low in herbs and
shrubs habitat with (36.925), thus indicating possible
differences in species richness among habitats. The
dominance index with highest values in Shrubs and herbs
with (52.727) and found to be lowest in Agricultural field
with (16.363). The present study recorded maximum butterfly
species in Herbs and Shrubs (n=29, AM: 7.25,
SD:7.182,SE:3.591, df:3) which consist of 52.72%, followed
by grassland (n=17 AM: 3.40, SD: 1.673, SE: 0.748, df:4),
which consist of 30.90%, Agricultural field shows the
minimum number,(n=9, AM: 3.000, SD: 1.732, SE: 1.000, df:
2) which consist of 16.36% were observed during the study.
Fifty five species of butterflies were categorized under IUCN
status. Among butterflies, the one Rare species was found to
be the lowest (n=1) which consist of 1.81%, The Uncommon
species (n=12) which consist of 21.81% The Very common
species (n=16) which was 29.09% The Common species
found to be the maximum (n=26) which consist of 47.27%
were recorded during the present study.
The monthly-wise abundance of butterfly species was
recorded. During the survey 293 individuals belonging to 5
families were observed. The study observed that maximum
numbers of butterfly species in the month of January (n=80,
AM: 5.71, SD:6.069,SE: 1.622, df: 13) which consist of
27.30%, followed by December (n=76, AM:2.45, SD:1.912,
SE: 0.343, df:30) which consist of 25.93%, November (n=70,
AM: 4.61, SD:3.309, SE:0.854, df: 14) which consist of
23.89%, October (n=63, AM:4.50, SD:3.459, SE:0.924,
df:13) which consist of 21.50% and lowest digit of butterflies
observed in September (n=4, AM:1.00) which consist of
1.26% were recorded during the study. The study observed
~ 324 ~
Journal of Entomology and Zoology Studies
maximum numbers of butterflies belonging to the family
Pieridae followed by Papilionidae, Nymphalidae, Lycaenidae
and Hesperridae. Lemon emigrant (Catopsilia crocale)
belonging to Pieridae family was most dominant species
followed by Common crow (Euploea core), Common
emigrant (Catopsilia Pomona) and minimum numbers of
butterflies like Bright babial blue (Papilio ulysses), Malayan
(Megisba malaya) were observed during the study. The
present study also documented the butterfly with the host
plant species. The study area was dominated by plant species
belonging to the families Annonaceae, Apocynaceae,
Fabaceae, Malvaceae, Acanthaceae, Rubiaceae, Urticaceae,
Tiliceae, Euphorbiaceae, Passifloraceae, Poaceae, includes
Ficus sp, Calotropis sp, Tridax sp, Polyalthia longifolia,
Cassia fistula, Tabernaemontana sp, Alstonia scholaris, Ixora
sp, Lantana camara, Cleome viscose, Aegle sp, Citrus sp,
Terminalia arjuna, Murraya sp, Pisidium guajava, Areca
catechu, Cocos nucifera, Mangifera indica, Hibiscus sp,
Zizyphus jujuba, Justicia sp, Sida sp, Nerium sp, Mussaenda
frondosa, Cosmos sp, Zinnia sp, Bougainvillea sp and grasses.
4. Discussion [29] reported that overall 79 species of butterflies belongs to
five families including family Nymphalidae with Maximum
of 40 species followed by Lycanidae 13 varieties,
Papilionidae 9 species, 7 Hesperidae species under the five
different habitats like Grassland, Herbs and shrubs, Pond,
Agrifield and Garden field. We observed 55 species of
butterflies belonging to five different families. The family
Nymphalidae was found to maximum with 27 species,
followed by Papilionidae 10 species, Pieridae 10 species,
Lycanidae 7 species and one Hesperiidae species during the
study in Pallassana village, Palakkad district. The family
Nymphalidae (Brush-footed) outnumbered with maximum
species, this is because of their ecological adaptation [45],
speciation and high dispersal ability [46]. This is because their
polyphagous nature which helps them to inhabit in all habit.
Their dominance is also because of their active flying nature
and they can search a large area of resources [47]. The study
area documented maximum butterfly species in the family
Nymphalidae in herbs and shrubs habitat with 29 species,
followed by the habitat Grassland 17 species and Agricultural
field 9 species [29]. reported that overall 79 species of
butterflies belonging to 5 different families and 5 different
habitats like Grassland, Trees & shrubs, Pond, Agrifield,
Garden field. The butterfly diversity and abundance is highly
correlated with the availability of food plants and assemblage
of plant varieties in the habitat [21] (Kunte, 2000).
The present study area is dominated by plant species
belonging to families Annonaceae, Apocynaceae, Fabaceae,
Malvaceae, Acanthaceae, Rubiaceae etc. namely Ficus sp,
Calotropis sp, Tridax sp, Polyalthia longifolia, Cassia fistula,
Tabernaemontana sp, Alstonia scholaris, Ixora sp, Lantana
camara, Cleome viscosa, Aegle sp, Citrus sp, Terminalia
arjuna, Murraya sp, Psidiu.m guajava, Areca catechu, Cocos
nucifera, Mangifera indica, Hibiscus sp, Zizyphus jujuba,
Justicia sp, Sida sp, Nerium sp, Mussaenda frondosa, Cosmos
sp, Zinnia sp, Bougainvillea sp and grasses. Floral preference
in polinatiors may vary from species to species. The
abundance of butterfly species population depends on the
availability of positive tropical climate and topographic
features of the regions [48-50]. The butterfly diversity correlates
with the larval host plants and adult nectar plants. Factors like
predators, parasites and rainfall are major cause of influence
on butterfly abundance in particular habitat [51]. The study
area recorded 55 species of butterflies, were categorized into
Rare with 1 species, and followed by Uncommon with 12
species, Very common 16 species and Common with 26
species [52]. Reported the percentage of butterfly status of
presence or absence were Common (C), Very common (VC),
Uncommon (UC), Rare (R) [53]. Had recorded 46 species of
butterflies throughout Chennai city including Guindy National
park, [29] recorded that 79 butterfly species into 3 categories.
Rare with 3 species, Uncommon 27 species and Common 49
species.
The study area recorded maximum abundance of butterflies in
the month of January with 80 species followed by December,
November, and less butterfly species found in September
month which constitute of 4 species. Lemon emigrant
(Catopsilia crocale) belonging to Pieridae family was most
dominant species followed by Common crow(Euploea core),
Common emigrant(Catopsilia Pomona) and minimum
numbers of butterflies like Bright babial blue (Papilio
ulysses), Malayan (Megisba malaya) were observed during
the study. Diversity and abundance of butterflies correlate
with the flowering phenology of plants [54-55, 21]. The
abundance of butterfly diversity in different ecosystem is
directly proportional to the type and variety of flowers and
number of plants in a particular area. Study revealed that
family Nymphalidae, Papilionidae and Pieridae species
highest during October to January due to availability of
highest nectar during the season. Butterflies are common for
only a few months and rare or absent in other parts of the
year. Butterflies are sensitive to the changes in the habitat and
climate, which influence their distribution and abundance [56].
Habitat destruction, degradation, fragmentation, grazing,
forest fires and application of pesticides affect the population
of butterflies. In urban areas, many species of butterflies
depends on remnant vegetation or secondary forest for their
survival [57-58]. Mostly all wildlife faunal species are fast
disappearing due to decrease greenery areas and increase of
pollution. This ecosystem destruction directly affects the
destruction of butterfly diversity in that area [59-60]. Abundance
of butterflies usually indicates a healthier ecosystem.
Butterflies also serve as major pollinators of both wild and
cultivated plants. Although we cannot completely nullify the
ill effects of urbanization and development, we can at least try
to reduce them by planting endemic trees and plants
supporting the local wildlife. This will make sure that at least
the common species will not go on to the verge of extinction.
5. Conclusion
Due to lack of suitable management, unsustainable utilization
of natural resources, deforestation and urbanization,
uncontrolled use of pesticides, in-organic manures,
environmental pollution leads to the destruction of host plant
might be adversely affect the existence of both insects and
floral diversity of the area. By planting endemic trees and
plants supporting the local wildlife which will make at least
the common species will not go on to the verge of extinction.
In addition, further research will be needed for documentation
of butterfly species which gives future conservation of
butterflies in Kerala.
6. Acknowledgement
I thank Ms. R. Laksmipriya and Ms. Adhira. S for helping me
to identify the butterfly species.
~ 325 ~
Journal of Entomology and Zoology Studies
7. Figure
7.1 Plate
1. Glassy blue tiger 2. Lemon pansy 3. Striped tiger 4. Tawny coaster 5. Plain tiger 6. Chocolate pansy 7. Blue tiger 8. Yellow pansy 9. Common
evening brown 10. Dark evening brown 11. Great evening brown 12. Common bush brown 13. Dark banded bush brown 14. Common baron
15. Joker 16. Danaid egg fly.
1 4 2 3
5 6 7 8
9 10
00
0
11 12
13 14
4
15 16
~ 326 ~
Journal of Entomology and Zoology Studies
7.2 Plate
17. Great egg fly 18. Blue pansy 19. Dark blue tiger 20. Common four ring 21. Common castor 22. Common crow 23. Common sailor 24. Short
banded sailor 25. Common palm fly 26. Niligiri blue tiger 27. Anomalous nawab 28. Crimson rose 29. Common Mormon 30. Common Mormon
31. Common Mormon 32. Common jay.
32 30 29
28
31
25
24 23 22 21
17 19 18 20
26 29
~ 327 ~
Journal of Entomology and Zoology Studies
7.3 Plate
33. Tailed jay 34. Lime butterfly 35. Blue mormon 36. Common rose 37. Citrus swallow tail 38. Mottled emigrant 39. Common emigrant
40. Small grass yellow 41. Common grass yellow 42. Common jezebel 43. Cabbage butterfly 44. Psyche 45. Common wanderer 46. Crimson tip
47. Lemon emigrant 48.Common cerulean
46 47 48 45
44 43 42 41
37 38 39 40
33 34 35 36
~ 328 ~
Journal of Entomology and Zoology Studies
7.4 Plate
49. Small cupid 50. Common silver line 51. Forgot me not 52. Common pier rot 53. Malayan 54. Pea blue 55. Pea blue.
8. Reference
1. Tiple AD, Deshmukh VP, Dennis RLH. Factors
influencing nectar plant resource visits by butterflies on a
university campus, implications for conservation, Nota
Lepidopteralogica. 2006; 28:213-224.
2. Mac Nally R, Fleishman E. A successful predictive
model of species richness based on indicator species
Conservation Biology. 2004; 18:646-634.
3. Pollard E. Monitoring butterfly numbers In Goldsmith
FB (Ed.) Monitoring for Conservation and Ecology,
Chapman and Hall, London, 1991, 275.
4. Blair RB. Birds and Butterflies along an Urban Gradient
Surrogate Taxa for Assessing Biodiversity Ecological
Applications. 1999; 9:164-170.
5. Kunte K. Seasonal patterns in butterfly abundance and
species diversity in four tropical habitats in the northern
Western Ghats Journal of Bioscience. 1997; 22:593-603.
6. Mennechez NG, Schtickzelle N, Baguette M.
Metapopulation dynamics of the bog fritillary butterfly,
comparison of demographic parameters and dispersal
between a continuous and a highly fragmented landscape
Landscape Ecology. 2003; 18:279-291.
7. Padhey AD, Dahanukar N, Paigankar M, Deshpande M,
Deshpande D. Season and landscape wise distribution of
butterflies in Tamhini Northern Western Ghats India
Zoo’s Print Journal, 2006; 21:2175-2181.
8. Jha CS, CBS Dutt, KS Bawa. Deforestation and land use
changes in Western Ghats India. Current Science. 2000;
79:231-238.
9. Wilson WO. The Diversity of life Norton. NY USA,
1992.
10. Benton TG. Biodiversity and biogeography of Handerson
Island insects. Biol. J Linn. Soc. 1995; 56:245-59.
11. Heppner J. Classification of Lepidoptera Part I
Introduction Holarctic Lepidoptera. 1998; 5:148.
12. Gaonkar H. Butterflies of Western Ghats India including
Sri Lanka A biodiversity assessment of threatened
mountain system. A report submitted to Center for
Ecological Sciences. IISc Bangalore, 1996, 86.
13. D’ Abreu EA. The Central Provinces Butterfly List.
Records of the Nagpur Museum Number VII
Government Printing City Press, 1931, 39.
14. Tiple AD. Butterflies of Vidarbha region, Maharashtra
State, central India, Journal of Threatened Taxa. 2011;
3(1):1469-1477.
15. Issac Kehimkar. The Book of Indian Butterflies. Bombay
N at. Hist. Soc Mumbai, 2011.
16. Kunte K. Patterns of butterfly, bird and tree diversity in
the Western Ghats Curr. Sci. 1999; 77:577-586.
17. Kocher SD, EH Williams. The diversity and abundance
of North American butterflies vary with habitat
disturbance and geography. Journal of Biogeography.
2000; 27:785-794.
18. Smetacek P. Record of Plebejus eversmanni (Stgr.) from
India, J. Bombay Nat. hist. Soc. 1992; 89:385-386.
19. Gay. Common Butterflies of India. WWF India and
Oxford University Press Mumbai India, 1992.
20. Evans WH. The identification of Indian Butterflies
Bombay Natural History Society Bombay, 1932.
21. Kunte K. Butterflies of Peninsular India Universities
Press (Hyderabad) and Indian Academy of Sciences
(Bengaluru), 2000, 270.
22. Palot MJ, Balakrishnan VC, Kalesh S. An updated
checklist of butterflies of Kerala, with their Malayalam
names. Malabar Trogon. 2012; 9(3):22-29.
23. Mathew G, Rahamathulla VK. Studies on the butterflies
of Silent Valley National Park Entomon. 1993;
18(3):185-192.
24. Sudheendrakumar VV, Binoy CF, Suresh PV, Mathew G.
Habitat associations of butterflies in the Parambikulam
54 53 55
50 51 52 49
~ 329 ~
Journal of Entomology and Zoology Studies
Wildlife Sanctuary, Kerala, India, J Bombay Nat. Hist.
Soci. 2000; 97:193-201.
25. Arun PR. Butteflies of Siruvani forests of Western Ghats
with notes on their seasonality, Zoo’s Print Journal. 2003,
18(2).
26. Ambrose DP, Raj DS, Butterflies of Kalakad-
Mundanthurai Tiger Reserve Tamil Nadu Zoo’s Print
Journal, 2005, 20(12).
27. Eswaran R, Pramod P. Structure of butterfly community
of Anaikatty Hills Western Ghats Zoo’s Print Journal,
2000; 8:1939-1942.
28. Prasad GP, Prathibakumari V, Lizby AM. Butterflies of
Kerala University Campus Thiruvananthapuram Kerala
3rd Asian Lepidoptera Conservation Symposium and
Training Programme, 2010, 25-29.
29. Lekshmi Priya, Varunprasath Krishnaraj, Janaranjini
Sutharsan, Lakeshmanaswamy. Studies on butterfly
diversity in Adichanalloor Village Kollam District
Kerala. Journal of Entomology and Zoology Studies.
2017; 5(5):73-81.
30. Myers N. The Biodiversity challenge expanded hot spots
analysis environmental. 1990; 10:243-256
31. Rosin ZM, Myczko L, Piotr S, Lenda M, Moron D,
Sparks TH, Tryjanowski P. Butterfly responses to
environmental factors in fragmented calcareous
grassland, Journal of Insect Conservation. 2012; 16:321-
329.
32. Blair RB, Launer AE. Butterfly diversity and human land
use Species assemblages along an urban gradient
Biological. Conservation. 1997; 80:113-125.
33. Stefanescu C, Herrando S, Paramo F. Butterfly species
richness in the north-west Mediterranean Basin: The role
of natural and human induced factors, Journal of
Biogeography. 2004; 31:905-915.
34. Clark PJ, Reed JM, Chew FS. Effect of urbanization on
butterfly species richness, guild structure and rarity
Urban Ecosystem. 2007; 10:321-337.
35. Pocewicz A, Morgan P, Eigenb rode SD. Local and
landscape effects on butterfly density in northern Idaho
grasslands and forests, J Insect Conserv. 2009; 13:593-
601.
36. Bastin L. The distribution of plant species in urban
vegetation fragments Landsc Ecol. 1999 ; 14:493-507
37. Hall RI, Leavitt PR, Quinian R, Dixit AS, Smol JP.
Effects of agriculture, urbanization and climate on water
quality in the northern green plain Limnol Oceanogr.
1999; 44:731-759.
38. McKinney ML. Urbanization, biodiversity and
conservation Bioscience. 2002; 52:883-890.
39. Singh SK, Srivastava SP, Tandon P, Azad BS. Faunal
diversity during rainy season in reclaimed sodic land of
Uttar Pradesh India J Environ. Biol. 2009; 30:551-556.
40. Garg RK, Rao RJ, Saksena DN. Water quality and
conservation management of Ramsagar reservoir Datia
Madhya Pradesh. J Environ. Bio. 2009; 30:909-916.
41. Tilman D, Fargione J, Wolff B, D’Antonio C, Dobson A,
Howarth R. Forecasting agriculturally driven global
environmental change Science. 2001; 292:281-284.
42. Scriber JM, Tsubaki Y, Lederhouse RC (eds).
Swallowtail Butterflies Their Ecology and Evolutionary
Biology Scientific Publishers Gainesville Florida, 1995,
319-344.
43. Ishii M. Transect count of butterflies In Decline and
Conservation of Butterflies in Japan II, 1993, 91-101
44. Jiggins CD, McMillan WO, Neukirchen W, Mallet J.
What can hybrid zones tell us about speciation Biol. J
Linn. Society. 1996; 59:221-242.
45. Adler GH, Dudley R. Biogeography of Milkweed of Milk
butterflies Nymphalidae Danainae and mimetic patterns
on patterns on tropical pacific archipelagos. Biol. J Linn.
Society. 1996; 57:317-326.
46. Forsayeth RW. Life history of sixty species of
Lepidoptera observed in Mhow Central India.
Transactions of the Entomological Society of London.
1884; 3:377-419.
47. Faegri K, Vander-Pijl L. The principles of pollination
ecology Pergamon Press London Ravindra M,
Viswantathan S, and Ram GM. Checklist of butterfly
species of Osmania University Campus Hyderabad,
Zoo’s Print journal, 1996, 11(10).
48. Tiple AD, Khurad AM. utterfly species diversity, habitats
and seasonal distribution in and around Nagpur City,
Central India, World Journal of Zoology. 2009; 4(3):153-
167.
49. Subba RC, Atluri JB, Venkata Ramana SP, Meer BG.
The butterfly fauna of Vishakapatanam in South India,
Tiger. 2006; 30:29-32.
50. Hogsden KL, Hutchinson TC. Butterfly assemblages
along a human disturbance gradient in Ontario Canada
Canadian Journal of Zoology. 2004; 82(5):739-748.
51. Evangeline D, Santhi S. Butterfly diversity at Guindy
National Park in Metropolitan City of Chennai Tamil
Nadu South India Journal of Entomology and Zoology
Studies. 2017; 5(4):1361-1368.
52. Thangapandian MA, Ganesh P, Ramaraj C, Selvakumar,
Janarthan S. Diversity and Status of Butterflies in the city
Chennai, Tamil Nadu Hexapoda Insecta indica. 2014;
21:1-9.
53. Gutierrez D, Mendez R. Phenology of butterflies in a
mountain area in northen Iberian Peninsual, Ecography.
1995; 18:209-219.
54. Watt WB, Hoch PC, Mills SG. Nectar source use by
Colias butterflies chemical and visual aspects, Oecologia.
1974; 14:353-374.
55. Wynter-Blyth MA. Butterflies of Indian Region Bombay
Natural History Society Bombay, 1957.
56. Blair RB, Launer AE. Butterfly diversity and human land
use: Species assemblages along an urban gradient
Biological Conservation. 1997; 80:113-125.
57. Saikia MK, Kalita J, PK Saikia. Ecology and
conservation needs of nymphalid butterflies in disturbed
tropical forestofeastern Himalayan biodiversity hotspot
Assam India International Journal of Biodversity
Conservation. 2009; 1(8):231-250.
58. Sreekumar PG, Balakrishnan M. Habitat and altitude
preferences of butterflies in Aral am Wildlife Sanctuary,
Kerala International Society of Tropical Ecology. 2001;
42(2):277-281.
59. Thomas JA. Monitoring change in the abundance and
distribution of insects using butterflies and their indicator
groups, Philosophical Transactions of the Royal Society.
2005; 360:339-357.