session 2.2 floral & avifaunal composition - konkan coast
TRANSCRIPT
Floral and avifaunal composition, richness and diversity of traditional agroforestry homegardens in
Konkan Coast of Maharashtra.
Kumarsukhadeo P. Gadekar (University of Wales, Bangor, UK)Douglas L. Godbold (University of Natural Resources and Life Sciences,
Vienna, Austria)
Tropical homegardens: multi functionality and benefits
INTRODUCTION
Agriculture Homegardens Mangrove and fishing
Mangrove Mango plantations Livestock
Grassland Casuarina beaches Moist topical forest
Causes of land-use conversion in Konkan coastof maharashtra Coconut plantation
Shrimp farming Land conversion Chira mining
Loss of Casuarina beach Fuelwood Roads
Illegal fellings
ELECTRICITY STARVED MAHARASHTRA STATE
13 power generation project along Konkan coast:
26,608 MW
Jaitapur nuclear power project := 10,000 MW
Approved by the High Court stating that “The nuclear
power project stands higher footing than biodiversity
and public opposition as it is going to supply power to
millions of peoples”.
Risks and benefits still in closed lunch box
Geographical coordinates:16˚ 30' to 16˚ 43' N latitudes
&73˚ 19' to73˚30' E longitudes
Birds
Flora
Flora: A quadrate sampling technique
Birds: A point transect method based on distance sampling
Anacardium occidentale
Artocarpus heterophyllus
Curcuma longa
Michelia champaca
Acalypha hispida
Piper nigrum Ensete superbum Dioscoria alata
Dioscoria alataHeliconia rostrata
Mucuna pruriens
Rauvolfia serpentine
Floral results Total 206 plant species Dominant: Fabaceae,
Apocynaceae, Cucurbitiaceae , Ceasalpiniaceae, Poaceae , Euphorbiaceae, Moraceae and Verbenaceae .
Fruit, medicinal plants, ornamental, timber, fuelwood, spices etc.
Tree Shrubs Herb Climber0
10203040
02040608010088
48 4426
No.
of f
amili
es
No.
ofg
spe
cies
Mode of regeneration
Cultivated + natural regeneration
Natural regeneration
Cultivated
81 72 53
0 200 400 600 800 1000 1200 1400 1600 18000
102030405060708090
100
Tree: Sobs (Mao Tau) Shrub: Sobs (Mao Tau)Herb: Sobs (Mao Tau) Climber: Sobs (Mao Tau)
Abundance
Spec
ies
rich
ness
Fig. 6
Sample based species accumulation or rarefaction curves (Sobs) for the different components of the overall plant species assemblage’s verses abundance in homegardens vegetation.
Component Shannon Weaver index (H’)
Simpsons index (λ)
Simpsons index of diversity (1-λ)
Species evenness (E)
Tree 3.82 0.04 0.96 0.85
Shrub 3.32 0.05 0.95 0.85
Herb 3.48 0.04 0.96 0.92
Climber 3.00 0.06 0.94 0.92
Overall 4.76 0.02 0.98 0.82
Cocos nucifera, Dendrocalamus strictus, Mangifera indica, Psidium guajava, Areca catechu, Anacardium occidentale, Artocarpus heterophyllus, Jatropha curcas, Musa paradisiaca, Hibiscus rosa-sinensis, Gliricidia sepium, Colocasia esculenta, Hemidesmus indicus, Trichosanthes cucumerina, Piper longum, Piper nigrum and Garcinia indica, Murraya koenigii, Tectona grandis, Moringa oleifera and Manilkara zapota.
Bird study results 76 bird species Dry season (62) and monsoon season (59). There are seven bird species only occurred in Monsoon season which
never recorded in dry season (SEASONAL MIGRATORY).
jungle Crow, baya Weaver, brahminy Kite, red wattled, spotted Dove, Indian Myna, rose ringed-parakeet, red whiskered Bulbul, red vented Bulbul, Indian pied Hornbill, large gray Babbler, black Drongo, small Bee-eater, jungle bush Quail, black shouldered Kite, Indian house Crow, cattle Egret etc.
Malabar Trogon, spotted Owlet, Indian Peafowl, Hoopoe, white breasted Waterhen, black Bulbul, Indian pied Wagtail, red Munia, yellow fronted Barbet, purple Sunbird, painted Spourfowl, tickells blue Flycatcher, white spotted fantail Flycatcher, Eurasian blackbird, common Kestrel, rosy Starling, night Heron, Indian Pitta are rare bird species
0 100 200 300 400 500 6000
10
20
30
40
50
60
70
Dry season: Sobs Mao TauMonsoon season: Sobs Mao Tau
Abundance
Spec
ies
richn
ess
Parameter Dry season
Monsoon season
Abundance 452 567
Bird density ha-1 35.7 42.5
Detection probability/ha
66.6 75.8
Effective detection radius for point transects
27 26
Encounter rate 4.6 5
Shannon Weaver index (H’)
3.66 3.47
Simpsons index of diversity (1-D)
0.96 0.95
Simpsons index of dominance (D)
0.036 0.046
Species evenness (E)
0.89 0.85
Predicted sample based Rarefaction curves (EstimateS 8.2.0 version) showing bird species richness verses abundance for homegardens, in the dry season. Solid lines represent species richness in the dry season and dotted lines represents species richness values in the monsoon season
Indian-Pied Hornbil
Red-Whiskered Bulbul
Lagger Falcon
Black-Hooded Oriole
Baya WeaverIndian Myna
Indian House Crow
White-Throated Kingfisher
Conclusion
The higher number of rare species in the study area is important for conservation point of view.
It is concluded that the bird analysis study site exhibits diverse homegarden habitat and is rich in bird species. The wide variety of the bird species like hornbills, woodpeckers, warblers, drongos, flycatchers, kingfishers, starlings, crows and kites indicates richness and diversity of the bird species in the study area.
Our study highlights the importance of conducting and documenting bird diversity at different land-use type. It is important to carry out repeated inventories of the Konkan coast in order to track regional and global changes in population of bird species.
The study demonstrates rich floral and avifaunal diversity of homegardens. Therefore, the priority should be given to the region for conservation and
sustainable management of floral biodiversity of homegardens, which is facing pressure from increasing population, land-use changes, deforestation and developmental activities.
The variation in species richness, dominance and diversity for homegardens vegetation components indicate dynamic nature.
Conclusion Although ornithological knowledge of the Western Ghats is significant,
understanding the avifaunal diversity is still important for conservation planning and restoring ecosystems in long term management. We therefore suggest further systematic and long term avian survey to document changes in overall species richness and diversity in Konkan coast of Western Ghats.
Being an ecological indicators as well as aesthetic reasons it is important to understand how birds are affected by human induced land-use changes. Therefore, it will help for better conservation planning of avifauna of the study area in the future.
The outcomes of our study will provide baseline data for monitoring and conserving the vegetation and avifaunal diversity of tropical homegardens vegetation and other land-use types.
The present study conclude that land clearing, land breaking and nuclear power project installation will affect the biodiversity and carbon balance. Therefore, the study suggests that it should not be started at Jaitapur for future environmental health, safety, public health, security and to avoid future hazards of loss of biodiversity.
THANKS A LOT