IMPORTANT BIRD AREAS PROGRAMME OF INDIA
www.ibcn.in
An effective way to save birds is to save the places where they live; the identification of such representative habitats is carried out through the Important Bird Areas Programme of BirdLife International. BirdLife International is a partnership of organisations working for the conservation of birds and their habitats and through these the diversity of all life. The Bombay Natural History Society [BNHS] is the BirdLife Partner Designate in India and is coordinating the programme in India. The Indian IBA Programme is being funded by the Royal Society for the Protection of Birds [RSPB], the BirdLife Partner in the United Kingdom.
IBAs are sites of international significance for bird conservation. They are part of a wider, integrated approach to conservation that embraces site, species and habitat protection and will be used to reinforce the existing protected areas network. They will contribute to the conservation of biodiversity as sites which are rich in birds are also likely to be rich in other species.
The IBA Programme will gather, use and disseminate information on key bird species and the sites that are important for them through active participation of people. The IBA programme will also try to involve communities living in and around IBAs in their conservation.
Aim
The IBA Programme aims to identify, document and advocate the protection and management of a network of sites that are important for the long-term viability of naturally occurring bird populations across the geographic range of those bird species for which a site-based approach is appropriate.
The IBA programme will produce inventories of internationally recognized sites vital for the conservation of birds. It will identify, document and protect a network of sites which covers all these habitats and species. Given that birds are good indicators of overall biological diversity, most IBAs will also be important for other animals and plants. The IBA programme aims to identify and promote the protection of networks of key sites for the conservation of birds and other Biodiversity in all regions of India.
The aims of the IBA Programme include to:
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Contribute in the development of national conservation strategies, highlight sites which are threatened or inadequately protected
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Help build regional and national networks of ornithologists and conservationists.
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Guide the work of international and national NGOs
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Influence global conventions, e.g. Biodiversity, Ramsar; etc.
The Indian IBA programme will also try to contribute in:
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Help identify high biodiversity areas
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Help identify future priorities for birds and biodiversity conservation action
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Provide decision makers with high quality biodiversity information for sustainable land and resource use
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Assist governments in the implementation of international agreements such as the Convention on Biological Diversity
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Provide material for education and training
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The National Biodiversity Strategy and Action Plan.
Site based approach
The Important Bird Areas (IBA) Programme of BirdLife International is a worldwide initiative aimed at identifying and protecting a network of critical sites for the conservation of birds. The IBA programme is a site-based approach, which identifies sites of international importance for the conservation of birds and other biodiversity and collates and disseminates key information. Information availability of the importance and location of such sites is fundamental to the success of a site based conservation strategy.
Birds are one of the best-researched taxa in India and a fairly reliable indicator of biodiversity loss. Given that birds are good indicators of overall biological diversity, most IBAs will also be important for other animals and plants. A significant proportion of bird (and other animal and plant species) can be effectively conserved by the protection of key sites, either as official protected areas (national parks and reserves) with necessary and appropriate management, and or through the promotion of sustainable land-use practices (Mallari et al. 1998).
Scope of the IBA Programme
The IBA Programme incorporates the conservation of species and the sites essential for their conservation it therefore covers the entire country and a wide range of habitats has a very wide scope.
Species
The programme not only covers the 79 Globally threatened birds in India (comprising of Critical Endangered, Vulnerable and Data Deficient and Conservation Dependent species) but also covers species that are endemic or have restricted ranges, congregatory birds and assemblages of species that are typical to a habitat or biome.
Habitats
As the programme covers a wide array of bird species, it also ranges across various habitats such as wetlands, islands, coastal areas, deserts, forests, grasslands and agricultural ecosystems.
Geographic range
The BNHS organised 9 regional workshops to identify IBAs for every state and union territory of India. With the exception of Daman and Diu & Chandigarh, IBAs have been identified for all the states and union territories of India, including those like Meghalaya for which there was very little data.
Limitations of the IBA approach
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The IBA approach only works for those species for which a site-based approach is appropriate. Bird species with highly dispersed or nomadic distributions may not be protected through this approach. Some bird species are not well protected by the IBA approach (such as large raptors, cranes and bustards, which are dispersed at low densities across wide areas and nomadic species).
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For others, the IBAs might be only appropriate across some of their ranges or for parts of their life cycles, (e.g. colonial nesting species that disperse extensively during the non-breeding season) (Barnes 1998).
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Any strategy for the long-term protection of biotic diversity should encompass evolutionary and biogeographic considerations. The IBA programme attempts to take this into account by selecting a network of sites that were spread through most habitats and in different areas of the species distributions. However sub-specific variation was not taken into account. Any future assessment should attempt to include sites where different morphs and subspecies (particularly endemic and restricted range subspecies) are located (Barnes 1998).
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The IBA programme is just one approach to bird conservation. It is not in the whole and the only answer. The IBA criteria are fairly stringent and many sites that are of undoubted local, provincial and national importance fail to qualify as IBAs. This does not mean that they are not important for conservation; on the contrary these sites often fulfill vital conservation roles at local scales. It must be emphasised that sites not designated as IBAs are not dispensable and their role in a wider land-use conservation strategy may be as vitally important as that of any IBA (Barnes 1998).
Process of IBA identification and Selection.
Literature Survey
The foundation of this project is laid in the data on bird numbers and distribution generated through the numerous field surveys and research programmes carried out in India during the last few decades. Exhaustive literature surveys were undertaken and information was gathered from various sources including national environmental organizations, individuals, scientists, protected areas staff, natural history museums, research institutions, universities and publications. Unpublished material held by research and conservation organizations were also analysed during this study. A draft list of 3000 sites was drawn up at the end of this process. This list included records of vagrancy and historical occurrence of bird species, this had to be filtered.
Workshops and consultation
Researchers, ornithologists, local forest officials, bird enthusiasts were consulted through workshops, meetings and correspondence to identify a list of IBAs throughout the country. Emphasis has been given to the participation of governmental and non-governmental conservation bodies and academic institutions. Regional workshops were held in which contributions have been made by a vast network of ornithologists, birdwatchers, personnel working for the forest departments, and conservation experts across India and the world. State coordinators of the Indian Bird Conservation Network have been involved in collating and assessing the data for each state in collaboration with Bombay Natural History Society.` The participants reviewed the draft list and added and deleted sites based on current information and possibility of occurrence of species at sites. The workshop list identified about a 1,000 sites.
Identification of gaps.
There was a lacuna of information from several areas in India and for certain species. Sites could not be identified for some species and states like Meghalaya, Mizoram and Nagaland and several districts from other states. This was mainly due to lack of data from these areas.
Surveys for sites and species
Surveys were then commissioned and successfully executed for data deficient species and areas in several states like Meghalaya, Mizoram, Nagaland, Maharashtra, Kerala, Orissa, and Bihar.
Capacity building training workshops
Some areas remained unexplored largely due to the lack of skilled manpower to execute the surveys. The Indian Bird Conservation Network conducted several training workshops in bird census techniques. A manual for bird census was also developed and distributed.
Site prioritisation
Three hundred and thirty five sites that are confirmed IBAs have been chosen from the workshop lists. The number of sites in this list is increasing as new information keeps coming in. These sites are identified on the basis of bird numbers and species complements that they hold, and are selected such that taken together they form a network throughout the species biogeographic distributions. This network may be considered, as a minimum essential to ensure the survival of these species across their ranges, should there occur a net loss of remaining habitat elsewhere through human or other modification. Therefore the consequences of the loss of any one of these sites may be disproportionately large. The continued ecological integrity of these sites will be decisive in maintaining and conserving birds for which a site based approach is appropriate. Legal protection, management and monitoring of these crucial sites will be important targets for action and, many but not all bird species may be effectively conserved by these means. Patterns of bird distribution are such that, in most cases it is possible to select sites that support many species (Heath and Evans 2000).
Circulation of Draft lists
Draft lists are continuously circulated to experts for comments and updating information. Several additional sites are being identified as IBAs as new information comes.
IBA Inventories
The Asian IBA Inventory is scheduled for publication in the year 2002, followed by the Indian IBA inventory in 2003. State IBA inventories for each state in India are also on the anvil. These inventories are intended to provide comprehensive information on IBA sites and species and to be used as an advocacy tool for site and species conservation to enable informed decision making.
Advocacy, awareness and involvement of local communities
The IBA process does not stop at identification and documentation of sites. It encourages widespread ownership of the concept especially at the grass root level. The IBA project also involves local communities living in and around IBA sites in their conservation.
Important Bird Areas and the National Biodiversity Strategy and Action Plan (NBSAP)
Both the National Biodiversity Strategy and Action Plan and IBA are complementary methods with biodiversity conservation as their common goal. The IBA relates to several aspects and components of the NBSAP and is featuring as a sub thematic rewiew note in the NBSAP.
Status of IBAs
IBAs are the first comprehensive study in which sites have been identified for bird conservation. 335 IBAs have been identified so far. This list however is dynamic and not a fixed list of sites. It is anticipated that several new IBAs will be identified.
Around 90% of IBAs in India are important for one or more of the 79 globally threatened species in India and 47% for the 74 restricted range species found in India. Almost all IBAs fall under at least one biome and hold some of the 374 bird species that fall in the biome criterion.
IBAs are also important for species that congregate in large numbers such as congregatory terrestrial birds, wintering and passage waterbirds and breeding seabirds almost 17%of IBAs have been identified for theses species. (For a list of IBAs Appendix VIII.)
International recognition
IBAs are recognised by intergovernmental bodies and international treaties such as the Biodiversity and Ramsar conventions. The Global Environment Facility recognises IBAs in their own strategies and action plans, while the European Union has used them as a basis for legal judgments (Heath and Evans 2000).
Some International conventions and programmes are particularly relevant to sites and species, these are: The Convention on Wetlands of International Importance, especially as Waterfowl habitat (Ramsar Convention), Convention on the Conservation of Migratory Species of wild animals (Bonn Convention), Convention on Biological Diversity and UNESCO's Man & Biosphere Programme (Evans 1994).
The IBA criteria are compatible with the Ramsar criteria set for wetlands of international importance, yet only 16 IBAs are Ramsar sites, IBAs that qualify the Ramsar criteria should be considered for designation as Ramsar sites for the internationally important numbers of waterbirds that they hold.
IBAs not covered under the protected area network
The 92 National Parks and 480 wildlife sanctuaries in India respectively cover 35,357.82 sq. km and 1,15,451& sq. km, which constitutes 4.58% of the country's 32,87,213 sq. km of geographic area (Kutty and Kothari 2001). A high proportion of IBAs in India does not fall within the protected areas system. With 45% of the IBAs still unprotected, IBAs should be designated under national laws where appropriate. While legal measures may not always guarantee protection on the ground, they demonstrate to all sectors of society and branches of government, the official recognition and importance of a site.
Bird species can be conserved by protection of sites, and by choosing the richest sites we can conserve many species at the same time, this also makes the best use of the scarce resources that are available for conservation. The Important Bird Areas (IBAs) process is about identifying and protecting those critical sites. IBAs form a network throughout a species’ range. As habitats become more threatened, this network will become increasingly important to make sure that these species survive across their ranges. IBAs may include the best examples of the species’ natural habitat.
Places where a wide variety of birds are found tend to have a wide variety of other forms of life. As IBAs are defined using birds, but they help to protect other wildlife as well.
The sites are selected using scientific methods, but it is also a very practical approach. The existing protected area network will form the backbone of network of IBAs and new sites will be proposed to fill the gaps. Ideally, each site should be large enough to support self-sustaining populations of as many of the species as possible for which it was identified. The IBA approach is only suitable for those bird species for which a site based approach is appropriate site-based approach, this approach however, does not suit all birds. Thus the IBA Programme is only one tool in the armory of conservation and needs to be combined with other conservation strategies in the wider environment.
Points to remember, IBAs:
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are places of international significance for the conservation of birds at the global, regional or sub-regional level,
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are practical tools for conservation,
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are chosen using standardised, agreed criteria applied with common sense,
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must, wherever possible, be large enough to support self-sustaining populations of those species for which they are important,
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are places which can be defined and distinguished from surrounding areas, and which are feasible to conserve,
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where possible preferentially include, where appropriate, existing Protected Areas,
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are not appropriate for all bird species and, for some, are only appropriate in parts of their ranges,
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should form part of a wider, integrated approach to conservation that embraces sites, species and habitat protection.
I. Categories and criteria to identify Important Bird Areas
The following categories and criteria are the standard guidelines for the identification of IBAs. These guidelines were used with scientific backup and with common sense. A site must meet at least one of the criteria described below (BirdLife International, undated).
(A1) Globally Threatened species: The site regularly holds significant numbers of a globally threatened species, or other species of global conservation concern. This category refers to species classified as globally threatened with extinction, Conservation Dependent or Data Deficient according to the new IUCN criteria for threatened status. The site qualifies if it is known, estimated or thought to hold a population of a species as categorized to this new IUCN criteria. Population-size thresholds for globally threatened species are set regionally, as appropriate, to help in site selection.
The word 'regular' and 'significant' in the criterion definition are intended to exclude instances of vagrancy, marginal occurrence, ancient historical records etc. 'Regularly' includes seasonal presence (and at longer intervals, if suitable conditions themselves only occur at extended intervals, e.g. temporary wetlands such as Chhari Dhand in Kutch district of Gujarat). However, sites that have the potential to hold threatened species, following habitat restoration work or re-introductions may also be considered. Near Threatened (NT) species can also be included in this category as defined and listed in (Collar et al. 1994).
(A2) Restricted Range Species: The site is known or thought to hold a significant component of the restricted-range species whose breeding distributions define an Endemic Bird Area (EBA) or Secondary Area (SA).
Restricted Ranges species are defined as all landbirds which have had, throughout historical times (i.e. post 1800 AD, in the period since ornithological recording began), a total global breeding range estimated at below 50,000 km2. Species with historical ranges estimated to be above this threshold, but which have been reduced to below 50,000 km2 by habitat loss or other pressures, were not covered because the EBA project seeks to locate natural areas of endemism for birds, which are also likely to be important for other unique animals and plants (although it is recognised that many species' ranges will have been severely altered by human impact prior to 1800 AD). Restricted range landbirds which have become extinct since 1800 AD were included in the analysis, because they have helped to identify areas which have concentrations of such taxa (Stattersfield et al. 1998).
Seabirds were excluded from the analysis because their distributions are determined by different factors to those which affect landbirds and other terrestrial taxa, and they are therefore considered to be best treated as a separate group for conservation purpose (Stattersfield et al. 1998).
Endemic Bird Areas relevant to India:
1. Western Ghats
2. Andaman Islands
3. Nicobar Islands
4. Western Himalayas
5. Eastern Himalayas
6. Assam Plains
7. Southern Tibet ( Though the area primarily lies in Tibet, portions of it also extend into India)
Secondary Areas in India:
1. Eastern Andhra Pradesh
2. Southern Deccan plateau
3. Indus plains
4. Central Indian Forests
5. North Myanmar lowlands (mainly in Myanmar but also includes lowlands of India)
(For a list of Restricted range bird species in India that qualify this Criteria please see Appendix III.)
(A3) Biome-Restricted Assemblages: The site is known or thought to hold a significant component of the group of species whose distributions are largely or wholly confined to one biome.
A biome may be defined as a major regional ecological community characterised by distinctive life forms and principal plant species (Crosby 1997). No system of global biome classification has been found which can be adequately used as a basis for generating bird species lists. Therefore, it is necessary that we should have a regional approach, which may result in inter-regional differences but at the over all scale at which biome division are recognised may be comparable.
This category applies to groups of species with largely shared distributions of greater that 50,000 km2, which occur mostly or wholly within all or part of a particular biome and are, therefore, of global importance.
The major biomes in India as classified by BirdLife International are as follows:
BIOME 05: EURASIAN HIGH MONTANE (ALPINE AND TIBETAN)
BIOME 07: SINO-HIMALAYAN TEMPERATE FOREST
BIOME 08: SINO-HIMALAYAN SUBTROPICAL FOREST
BIOME 09: INDOCHINESE TROPICAL MOIST FORESTS
BIOME 10: INDIAN PENINSULA TROPICAL MOIST FOREST
BIOME 11: INDO-MALAYAN TROPICAL DRY ZONE
BIOME 12: INDO-GANGETIC PLAINS
BIOME 13: SAHARO-SINDIAN DESERT
(For a list of biome wise distribution of bird species that qualify this Criteria for each biome please see Appendix IV.)
(A4) Congregations: This category applies to those species that are vulnerable because they congregate at sensitive sites when breeding or wintering, or while on passage. The term 'water-bird' is used here in the same sense as the Ramsar Convention uses 'waterfowl' and covers the list of families more precisely defined by Wetlands International in Rose & Scott 1994. Congregatory non-waterbird species (A42) include both terrestrial species and those families of seabird not covered by Rose & Scott 1994 such as Procellaridae, Hydrobatidae, Pelecanididae, Phaethontidae, Sulidae, and Fregatidae.
This category has four sub-division:
(A4i). Site known or thought to hold, on a regular basis, ³ 1% of a biogeographic population of a congregatory waterbird species. For the thresholds of this criterion, relevant flyway populations are combined to produce biogeographic population estimates.
(A4ii) Site known or thought to hold, on a regular basis, ³ 1% of the global population of a congregatory seabird or terrestrial species. This category covers non-water bird or terrestrial birds or sea birds are not included by Rose & Scott 1994.
(A4iii) Site known or thought to hold, on a regular basis, ³ 20,000 waterbirds or ³ 10,000 pairs of seabirds of one or more species. Use of this criterion is discouraged where data quality permits A41 and A42 to be used.
(A4iv) Site known or thought to be a 'bottleneck site' where at least 20,000 storks (Ciconiidae), raptors (Accipitriformes and Falconiformes) or cranes (Gruidae) pass regularly during spring or autumn migration.
Table 1 Categories of criteria for site selection under the Ramsar Convention (adopted at the Conference of the Parties, 7 May 1999).
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Representative, rare, or unique example of a natural or near-natural wetland type found within the appropriate biogeographic region.
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Supports vulnerable, endangered, or critically endangered species or threatened ecological communities.
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Supports populations of plant and/or animal species important for maintaining the biological diversity of a particular biogeographic region.
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Supports plant and/or animal species at a critical stage in their life cycles, or provides refuge during adverse conditions.
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Regularly supports 20,000 or more waterbirds.
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Regularly supports 1% of the individuals in a population of one species or subspecies of waterbird.
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Supports a significant proportion of indigenous fish subspecies, species or families, life-history stages, species interactions and / or populations that are representative of wetland benefits and /or values and thereby contributes to global biological diversity.
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An important source of food for fishes, spawning ground, nursery and/or migration path on which fish stocks, either within the wetland or elsewhere, depend.
Criteria A41 and A43 identify wetlands of international importance (Ramsar Sites), being similar to Ramsar criteria 5 and 6 respectively in the table1.
'Water bird' as 'seabird'
The term 'waterbird' is used in the same sense as that used for 'waterfowl' under the Ramsar Convention.
'Biogeographic population'
'Biogeographic' is used in the sense of a zoogeographic realm, e.g. the Palearctic, which are large geographical regions in which the organisms present tend to be different from those of other realms. Thus such regions are characterized largely through the shared distribution patterns of many species. All 'populations' of a given species that are resident or migratory through this region are combined to form the ''biogeographic population'. We do not have sufficient flyway population information at the moment, but through the IBA programme we may be able to get good information.
1% thresholds and applying the criteria
1% threshold figures have been defined for all congregatory waterbird species, including species for which no thresholds are currently recognized under the Ramsar Convention. Wetlands International has collaborated in generating numberic thresholds from range estimates and from unpublished population data.
There is a logical inconsistency between criterion A41 for waterbirds (1% or more of the biogeographic population) and criterion A42 for seabirds (1% or more of global population of seabirds). It was felt, however, that the alternative of using 1% of the global population for waterbirds would, as well as departing from the criteria used under the Ramsar Convention, have insufficient biological justification, since relatively well defined, discrete flyway populations can be distinguished within Asia for many migratory waterbird species. Taking 1% of global population would over-emphasis waterbirds endemic to Asia, since many widely distributed species may rarely occur at congregations exceeding 1% of the global population, over much of their range.
A43 and A44 criteria are applied at the site level only, not to individual species.
The A44 criterion embraces sites over which flying migrants concentrate, e.g. at narrow sea-crossings, along mountain ranges or through mountain passes. Conservation of the land beneath may be necessary to protect the site and its birds from threats such as shooting and the construction of lethal obstacles such as power-lines and high radio-masts. Also included under A44 are migratory stop-over sites and nocturnal roosts which may not hold 20,000 or more storks, raptors or cranes at any one time but which, nevertheless, do hold such numbers over a relatively short period due to the rapid turnover of birds on passage.
How do the IBA criteria relate to the identification of Ramsar sites under the Ramsar Convention
The Ramsar (or Wetlands) Convention defines a wetland as 'an area of marsh, fen, peatland or water, whether natural or artificial, permanent or temporary, with water that is static or flowing, fresh, brackish or salt, including areas of marine water the depth of which at low tide does not exceed 6m' (Article 1). Article 2.1 of the Convention also states that 'the boundaries of each wetland […] may incorporate riparian and coastal zones adjacent to the wetlands, and islands or bodies of marine water deeper than 6m at low tide lying within the wetlands, especially where these have importance as waterfowl habitat'.
The criteria for identifying wetlands of international importance under the Ramsar Convention, as adopted at the Conference of the Parties on 7 May 1999, fall into eight categories given in the tablexxx. There is a strong relationship between the Ramsar categories for waterbirds and the IBA criteria. Ramsar criterion categories 6 was one of the main criteria used in identifying IBAs. It has been used for both non-breeding populations of waterbirds and for breeding concentrations of some congregatory species. Average (preferably five years) of seasonal peak numbers have been used to assess whether the 1% threshold is met, although this was not possible for every area or country due to lack of five-year data sets. Ramsar criterion category 5 has also been applied to many IBAs. However it has not always been applied as an independent criterion, because criterion 6 was given preference where suitable data were available. Many IBAs also comply with Ramsar criteria categories 2,3 and 4 particularly wetland sites (such as Keoladeo National Park) that are important for birds other than waterbirds.
Thus, overall, IBA criteria comply with the Ramsar criteria for birds. However, one divergence is that IBA criteria A41 may be applied to congregations of waterbirds in grassland and marine habitats (not classifiable as wetland habitat under the Ramsar definition). Some of the congregatory sites especially 1% thresholds for some waterbirds may be met in grasslands areas (Ramsar criterion 6), the Ramsar wetland definition excludes these sites from consideration under the Convention, therefore their eligibility for designation as Ramsar Sites has be considered on a case-by-case basis.
Appendix I
Important Bird Areas: summary of global categories and criteria
|
Category |
Criterion |
Notes |
|
Globally threatened species |
The site regularly holds significant numbers of a globally threatened species, or other species of global conservation concern. |
The site qualifies if it is known or thought to hold a population of a species categorized as Critical, Endangered, Vulnerable, Conservation Dependent or Data Deficient. |
|
Restricted-range species |
The site is known or thought to hold a significant component of the restricted-range species whose breeding distributions define an Endemic Bird Area (EBA) or Secondary Area (SA). |
The site also has to form one of a set selected to ensure that, as far as possible, all restricted-range species of an EBA or SA are present in significant numbers in at least one site and, preferably, more. |
|
Biome-restricted assemblage |
The site is known or thought to hold a significant component of the group of species whose distributions are largely or wholly confined to one biome. |
The site also has to form one of a set selected to ensure that, as far as possible, all species and habitats characteristic of a biome are adequately represented. |
|
Congregations |
(i) The site is known or thought to hold, on a regular basis, ³ 1% of a biogeographic population of a congregatory waterbird species.
Or |
This applies to waterfowl species as defined by Rose and Scott (1997). Thresholds have been set by combining flyway populations within Asia. For species lacking quantitative data, thresholds were set by estimating 1% of the Asian biogeographic population. |
|
|
(ii) The site is known or thought to hold, on a regular basis, ³ 1% of the global population of a congregatory seabird or terrestrial species.
Or |
This includes those seabird species not covered by Rose and Scott (1997). Where quantitative data were lacking, numerical thresholds were set by estimating 1% of the global population. |
|
|
(iii) The site is known or thought to hold, on a regular basis, ³ 20,000 waterbirds or ³ 10,000 pairs of seabirds of one or more species.
Or |
This is the Ramsar criterion for waterbirds, the use of which is discouraged wherever data are good enough to permit the use of (i) or (ii). |
|
|
(iv) The site is known or thought to exceed thresholds set for migratory species at bottleneck sites. |
Thresholds are set regionally or inter-regionally, as appropriate. |
Appendix II
Indian Red Data Book threatened bird species* (BirdLife International 2000)
|
|
SPECIES |
ENGLISH |
|
SPECIES |
ENGLISH |
|
1 |
Pelecanus crispus |
Dalmatian Pelican |
41 |
Gallinago nemoricola |
Wood Snipe |
|
2 |
Pelecanus philippensis |
Spot-billed Pelican |
42 |
Tringa guttifer |
Spotted Greenshank |
|
3 |
Fregata andrewsi |
Christmas Island Frigatebird |
43 |
Eurynorhynchus pygmeus |
Spoon-billed Sandpiper |
|
4 |
Ardea insignis |
White-bellied Heron |
44 |
Rhinoptilus bitorquatus |
Jerdon's Courser |
|
5 |
Ciconia boyciana |
Oriental Stork |
45 |
Rynchops albicollis |
Indian Skimmer |
|
6 |
Leptoptilos javanicus |
Lesser Adjutant |
46 |
Columba eversmanni |
Eastern Stock Pigeon |
|
7 |
Leptoptilos dubius |
Greater Adjutant |
47 |
Columba elphinstonii |
Nilgiri Wood-pigeon |
|
8 |
Oxyura leucocephala |
White-headed Duck |
48 |
Columba punicea |
Purple Wood Pigeon |
|
9 |
Anser erythropus |
Lesser White-fronted Goose |
49 |
Otus alius |
Nicobar Scops-owl |
|
10 |
Cairina scutulata |
White-winged Duck |
50 |
Heteroglaux blewitti |
Forest Owlet |
|
11 |
Anas formosa |
Baikal Teal |
51 |
Apus acuticauda |
Khasi Hills Swift |
|
12 |
Marmaronetta angustirostris |
Marbled Teal |
52 |
Aceros nipalensis |
Rufous-necked Hornbill |
|
13 |
Rhodonessa caryophyllacea |
Pink-headed Duck |
53 |
Aceros narcondami |
Narcondam Hornbill |
|
14 |
Aythya baeri |
Baer's Pochard |
54 |
Pycnonotus xantholaemus |
Yellow-throated Bulbul |
|
15 |
Haliaeetus leucoryphus |
Pallas's Fish-eagle |
55 |
Hypsipetes nicobariensis |
Nicobar Bulbul |
|
16 |
Accipiter butleri |
Nicobar Sparrowhawk |
56 |
Turdus feae |
Grey-sided Thrush |
|
17 |
Aquila clanga |
Greater Spotted Eagle |
57 |
Brachypteryx hyperythra |
Rusty-bellied Shortwing |
|
18 |
Aquila heliaca |
Eastern Imperial Eagle |
58 |
Brachypteryx major |
White-bellied Shortwing |
|
19 |
Falco naumanni |
Lesser Kestrel |
59 |
Saxicola macrorhyncha |
Stoliczka's Bushchat |
|
20 |
Megapodius nicobariensis |
Nicobar Megapode |
60 |
Saxicola insignis |
Hodgson's Bushchat |
|
21 |
Francolinus gularis |
Swamp Francolin |
61 |
Garrulax cachinnans |
Rufous-breasted Laughingthr |
|
22 |
Perdicula manipurensis |
Manipur Bush-quail |
62 |
Pellorneum palustre |
Marsh Babbler |
|
23 |
Arborophila mandellii |
Chestnut-breasted Partridge |
63 |
Spelaeornis badeigularis |
Mishmi Wren-Babbler |
|
24 |
Ophrysia superciliosa |
Himalayan Quail |
64 |
Spelaeornis longicaudatus |
Tawny-breasted Wren-babbler |
|
25 |
Tragopan melanocephalus |
Western Tragopan |
65 |
Stachyris oglei |
Snowy-throated Babbler |
|
26 |
Tragopan blythii |
Blyth's Tragopan |
66 |
Chrysomma altirostre |
Jerdon's Babbler |
|
27 |
Lophophorus sclateri |
Sclater's Monal |
67 |
Turdoides longirostris |
Slender-billed Babbler |
|
28 |
Catreus wallichi |
Cheer Pheasant |
68 |
Paradoxornis flavirostris |
Black-breasted Parrotbill |
|
29 |
Syrmaticus humiae |
Mrs. Mrs. Hume's Pheasant |
69 |
Prinia cinereocapilla |
Grey-crowned Prinia |
|
30 |
Pavo muticus |
Green Peafowl |
70 |
Chaetornis striatus |
Bristled Grass-Warbler |
|
31 |
Grus leucogeranus |
Siberian Crane |
71 |
Schoenicola platyura |
Broad-tailed Grassbird |
|
32 |
Grus monacha |
Hooded Crane |
72 |
Ficedula subrubra |
Kashmir Flycatcher |
|
33 |
Grus nigricollis |
Black-necked Crane |
73 |
Parus nuchalis |
Pied Tit |
|
34 |
Grus antigone |
Sarus Crane |
74 |
Sitta formosa |
Beautiful Nuthatch |
|
35 |
Rallina canningi |
Andaman Crake |
75 |
Amandava formosa |
Green Munia |
|
36 |
Heliopais personata |
Masked Finfoot |
76 |
Ploceus megarhynchus |
Finn's Weaver |
|
37 |
Ardeotis nigriceps |
Great Indian Bustard |
77 |
Gyps bengalensis |
White-backed Vulture |
|
38 |
Houbaropsis bengalensis |
Bengal Florican |
78 |
Gyps indicus |
Long-billed Vulture** |
|
39 |
Sypheotides indica |
Lesser Florican |
79 |
Gyps tenuirostris |
Slender-billed Vulture** |
|
40 |
Vanellus gregarius |
Sociable Lapwing |
|
|
|
|
|
|
|
|
|
|
*Species listed ad Critical (CR), Endangered (EN), Vulnerable (VU), Data Deficient (DD) or Conservation Dependent (CD) in the Asian Red Data Book. Near Threatened (NT) species have not been included.
* *The taxons of Indian Vulture (Gyps indicus) and Slender-billed Vulture(Gyps tenurostris) were initially described a separate species but have been treated as subspecies and known as Long-billed Vulture (Gyps indicus) since the early twentieth century. Recent studies have shown that the two forms are distinct species that are not even each other's closest relatives (BirdLife International 2001).
Appendix III
Endemic bird areas in India with the list of restricted range bird species found in them:
1. Western Ghats
|
1. |
Nilgiri Wood Pigeon |
Columba elphinstoni |
|
8. |
Blue-winged Parakeet |
Psittacula columboides |
|
9. |
Malabar Grey-Hornbill |
Ocyceros griseus |
|
10. |
Nilgiri Pipit |
Anthus nlghiriensis |
|
11. |
Grey-headed Bulbul |
Pycnonotus priocephalus |
|
12. |
Black-and-OrangeFlycatcher |
Ficedula nigrorufa |
|
13. |
Broad-tailed Grassbird |
Schoenicola platyura |
|
14. |
Small Sunbird |
Nectarinia minima |
|
15. |
Grey-breasted Laughingthrush |
Garrulax jerdoni |
|
16. |
Nilgiri Flycatcher |
Eumyias albicaudata |
|
17. |
Indian Rufous Babbler |
Turdoides subrufus |
|
18. |
Nilgiri Laughingthrush |
Garrulax cachinnans |
|
19. |
White-bellied Blue Flycatcher |
Cyornis pallipes |
|
20. |
White-bellied Shortwing |
Brachypteryx major |
|
21. |
White-bellied Treepie |
Dendrocitta leucogastra |
|
22. |
Wynaad Laughingthrush |
Garrulax delesserti |
2.Andaman Islands
|
1. |
Andaman Serpent Eagle |
Spilornis elgini |
|
2. |
Nicobar Megapode |
Megapodius nicobariensis |
|
3. |
Andaman Crake |
Rallina canningi |
|
4. |
Andaman Wood Pigeon |
Columba palumboides |
|
5. |
Andaman Cuckoo-dove |
Macropygia rufipennis |
|
6. |
Andaman Hawk-owl |
Ninox affinis |
|
7. |
Narcondam Hornbill |
Aceros narcondami |
|
8. |
Andaman Black Woodpecker |
Dryocopus hodgei |
|
9. |
Andaman Drongo |
Dicrurus andamensis |
|
10. |
Andaman Treepie |
Dendrocitta bayleyi |
|
11. |
White-headed Starling |
Sturnus erythropygius |
3.Nicobar Islands
|
1. |
Nicobar Serpent-eagle |
Spilornis minimus |
|
2. |
Nicobar Sparrowhawk |
Accipiter butleri |
|
3. |
Nicobar Megapode |
Megapodius nicobariensis |
|
4. |
Andaman Wood Pigeon |
Columba palumboides |
|
5. |
Andaman Cuckoo-dove |
Macropygia rufipennis |
|
7. |
Nicobar Parakeet |
Psittacula caniceps |
|
8. |
Andaman Hawk-owl |
Ninox affinis |
|
9. |
Nicobar Bulbul |
Hypsipetes nicobariensis |
|
10. |
White-headed Starling |
Sturnus erythropygius |
4.Western Himalayas
|
1. |
Himalayan Quail |
Ophrysia superciliosa |
|
2. |
Western Tragopan |
Tragopan melanocephalus |
|
3. |
Cheer Pheasant |
Catreus wallichii |
|
4. |
Brooke’s Leaf Warbler |
Phylloscopus subviridis |
|
5. |
Kashmir Flycatcher |
Ficedula subrubra |
|
6. |
Kashmir Nuthatch |
Sitta cashmirensis |
|
7. |
Orange Bullfinch |
Pyrrhula aurantiaca |
|
8. |
Spectacled Finch |
Callacanthis burtoni |
|
9. |
White-cheeked Tit |
Aegithalos leucogenys |
|
10. |
Tytler’s Leaf Warbler |
Phylloscopus tytleri |
|
11. |
White-throated Tit |
Aegithalos niveogularis |
5.Eastern Himalayas
|
1. |
Khasi Hills Swift |
Apus acuticauda |
|
2. |
Ward’s Trogon |
Harpactes wardi |
|
3. |
Chestnut-breasted Hill-Partridge |
Arborophila mandellii |
|
4. |
Blyth’s Tragopan |
Tragopan blythii |
|
5. |
Sclater’s Monal |
Lophophorus sclateri |
|
6. |
Beautiful Sibia |
Heterophasia pulchella |
|
7. |
Broad-billed Flycatcher Warbler |
Tickelli hodgsoni |
|
8. |
Brown-capped Laughingthrush |
Garrulax austeni |
|
9. |
Grey Sibia |
Heterophasia gracilis |
|
10. |
Hoary-throated Barwing |
Actinodura nipalensis |
|
11. |
Brown-throated Fulvetta |
Alcippe ludlowi |
|
12. |
Rufous-throated Wren-babbler |
Spaeleornis caudatus |
|
13. |
Rusty-bellied Shortwing |
Brachypteryx hyperythra |
|
14. |
Rusty-throated Wren Babbler |
Spelaeornis badeigualris |
|
15. |
Snowy-throated Babbler |
Stachyris oglei |
|
16. |
Streak-throated Barwing |
Actinodura waldeni |
|
17. |
Striped Laughingthrush |
Garrulax virgatus |
|
18. |
Tawny-breasted Wren-babbler |
Speleornis longicaudatus |
|
19. |
Wedge-billed Wren-babbler |
Sphenocichla humei |
|
20. |
White-naped Yuhina |
Yuhina bakeri |
|
21. |
Black-browed Leaf Warbler |
Phylloscopus canator |
6.Assam Plains
|
1. |
Manipur Bush Quail |
Perdicula manipurensis |
|
2. |
Blackbreasted Parrotbill |
Paradoxornis flavirostris |
|
3. |
Marsh Babbler |
Pellorneum palustre |
7.Southern Tibet
|
1. |
Giant Babax |
Babax waddelli |
Secondary Areas in India with a list of restricted range species found in them:
1. Eastern Andhra Pradesh
|
1. |
Jerdon's Courser |
Rhinoptilus bitorquatus |
2. Southern Deccan plateau
|
1. |
Yellow-throated Bulbul |
Pycnonotus xantholaemus |
3. Indus plains
|
1. |
Sind Sparrow |
Passer pyrrhonotus |
4. Central Indian Forests
|
1. |
Forest Owlet |
Heteroglaux blewitti |
5. North Myanmar lowlands
|
1. |
Chestnut-backed Laughingthrush |
Garrlux nuchalis |
Appendix 4 Biome wise distribution of bird species
BIOME 05: EURASIAN HIGH MONTANE (ALPINE AND TIBETAN)
BIOME 07: SINO-HIMALAYAN TEMPERATE FOREST
BIOME 08: SINO-HIMALAYAN SUBTROPICAL FOREST
BIOME 09: INDOCHINESE TROPICAL MOIST FORESTS
BIOME 10: INDIAN PENINSULA TROPICAL MOIST FOREST
BIOME 11: INDO-MALAYAN TROPICAL DRY ZONE
BIOME 12: INDO-GANGETIC PLAINS
BIOME 13: SAHARO-SINDIAN DESERT
BIOME 05: EURASIAN HIGH MONTANE (ALPINE AND TIBETAN)
LOCATION: The Altay-Sayan mountains in south-eastern Russia, western Mongolia and north-western China, the Tien Shan and Qinghai-Tibetan Plateau in China, and northern (Trans-Himalayan) Pakistan, India, Nepal, Bhutan, and Myanmar (extends westward into the central Asian republics, the Middle East and Europe). Open habitats at and above the tree-line, mainly above c.3,600 m.
KEY HABITATS: Scrub and open habitats at and above the tree-line, including alpine and subalpine scrub and grassland; inland cliffs and rocky slopes; scree and boulders; montane wetlands; gravel and sand plains.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Southern Tibet (EBA 133; 2 species); Eastern Tibet (EBA 134; 2 species); Southern Xinjiang mountains (SA 076; 1 species); Mongolian mountains (SA 077; 1 species); Northern Qinghai‑Tibetan plateau (SA 078; 1 species).
|
|
SPECIES |
ENGLISH |
|
1. |
Gyps himalayensis |
Himalayan Griffon |
|
2. |
Lerwa lerwa |
Snow Partridge |
|
3. |
Tetraogallus tibetanus |
Tibetan Snowcock |
|
4. |
Tetraogallus himalayensis |
Himalayan Snowcock |
|
5. |
Perdix hodgsoniae |
Tibetan Partridge |
|
6. |
Grus nigricollis |
Black-necked Crane |
|
7. |
Gallinago solitaria |
Solitary Snipe |
|
8. |
Gallinago nemoricola |
Wood Snipe |
|
9. |
Ibidorhyncha struthersii |
Ibisbill |
|
10. |
Larus brunnicephalus |
Brown-headed Gull |
|
11. |
Syrrhaptes tibetanus |
Tibetan Sandgrouse |
|
12. |
Columba leuconota |
Snow Pigeon |
|
13. |
Melanocorypha maxima |
Long-billed Calandra Lark |
|
14. |
Calandrella acutirostris |
Hume's Short-toed |
|
15. |
Anthus roseatus |
Rosy Pipit |
|
16. |
Anthus spinoletta |
Water Pipit |
|
17. |
Lanius tephronotus |
Grey-backed Shrike |
|
18. |
Prunella collaris |
Alpine Accentor |
|
19. |
Prunella himalayana |
Altai Accentor |
|
20. |
Prunella rubeculoides |
Robin Accentor |
|
21. |
Prunella fulvescens |
Brown Accentor |
|
22. |
Zoothera mollissima |
Plain-backed Thrush |
|
23. |
Turdus kessleri |
Kessler's Thrush |
|
24. |
Phoenicurus hodgsoni |
Hodgson's Redstart |
|
25. |
Phoenicurus erythrogaster |
White-winged Redstart |
|
26. |
Grandala coelicolor |
Grandala |
|
27. |
Saxicola insignis |
Hodgson's Bushchat |
|
28. |
Garrulax henrici |
Prince Henri's Laughingthrush |
|
29. |
Leptopoecile sophiae |
White-browed Tit-Warbler |
|
30. |
Phylloscopus fuligiventer |
Smoky Warbler |
|
31. |
Phylloscopus affinis |
Tickell's Warbler |
|
32. |
Phylloscopus griseolus |
Olivaceous Leaf Warbler |
|
33. |
Tichodroma muraria |
Wallcreeper |
|
34. |
Leucosticte nemoricola |
Plain Mountain-finch |
|
35. |
Leucosticte brandti |
Black-headed Mountain-finch |
|
36. |
Rhodopechys sanguinea |
Crimson-winged Finch |
|
37. |
Carpodacus pulcherrimus |
Beautiful Rosefinch |
|
38. |
Carpodacus rhodochlamys |
Red-mantled Rosefinch |
|
39. |
Carpodacus rubicilloides |
Streaked Rosefinch |
|
40. |
Carpodacus rubicilla |
Common Great Rosefinch |
|
41. |
Carpodacus puniceus |
Red-fronted Rosefinch |
|
42. |
Montifringilla nivalis |
White-winged Snowfinch |
|
43. |
Montifringilla adamsi |
Tibetan Snowfinch |
|
44. |
Montifringilla taczanowskii |
White-rumped Snowfinch |
|
45. |
Montifringilla ruficollis |
Rufous-necked Snowfinch |
|
46. |
Montifringilla blanfordi |
Plain-backed Snowfinch |
|
47. |
Pseudopodoces humilis |
Tibetan Ground-jay |
|
48. |
Pyrrhocorax graculus |
Yellow-billed Chough |
BIOME 07: SINO-HIMALAYAN TEMPERATE FOREST
LOCATION: The mountains bordering the Qinghai-Tibetan Plateau in southern and western China, northern Pakistan and India, Nepal and Bhutan, the mountains of Bangladesh, Myanmar, Taiwan, northern Laos, Thailand and Vietnam, and the Altay-Sayan and Tien Shan ranges in south-eastern Russia, western Mongolia and north-western China (extends westward into Afghanistan and the central Asian republics). Mainly between c.1,800 and 3,600 m.
KEY HABITATS: Broadleaf evergreen forest; Broadleaf deciduous, mixed broadleaf-coniferous and coniferous forest; Montane grassland.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Western Himalayas (EBA 128; 11 species); Central Himalayas (EBA 129; 3 species); Eastern Himalayas (EBA 130; 22 species); Qinghai mountains (EBA 135; 2 species); Shanxi mountains (EBA 136; 2 species); Central Sichuan mountains (EBA 137; 11 species); West Sichuan mountains (EBA 138; 3 species); Yunnan mountains (EBA 139; 3 species); Fan‑Si‑Pan and northern Laos (SA 082; 4 species).
|
|
SPECIES |
ENGLISH |
|
49. |
Tetraophasis szechenyii |
Buff-throated Partridge |
|
50. |
Arborophila torqueola |
Common Hill Partridge |
|
51. |
Ithaginis cruentus |
Blood Pheasant |
|
52. |
Tragopan satyra |
Satyr Tragopan |
|
53. |
Tragopan temminckii |
Temminck's Tragopan |
|
54. |
Pucrasia macrolopha |
Koklass Pheasant |
|
55. |
Lophophorus impejanus |
Impeyan Monal |
|
56. |
Columba hodgsonii |
Speckled Wood-pigeon |
|
57. |
Psittacula derbiana |
Derbyan Parakeet |
|
58. |
Indicator xanthonotus |
Yellow-rumped Honeyguide |
|
59. |
Dendrocopos darjellensis |
Darjeeling Woodpecker |
|
60. |
Dendrocopos himalayensis |
Himalayan Woodpecker |
|
61. |
Delichon nipalensis |
Nepal House-martin |
|
62. |
Prunella strophiata |
Rufous-breasted Accentor |
|
63. |
Prunella atrogularis |
Black-throated Accentor |
|
64. |
Prunella immaculata |
Maroon-backed Accentor |
|
65. |
Zoothera dixoni |
Long-tailed Thrush |
|
66. |
Zoothera monticola |
Larger Long-billed Thrush |
|
67. |
Turdus albocinctus |
White-collared Blackbird |
|
68. |
Turdus rubrocanus |
Chestnut Thrush |
|
69. |
Brachypteryx stellata |
Gould's Shortwing |
|
70. |
Luscinia pectoralis |
Himalayan Rubythroat |
|
71. |
Luscinia pectardens |
Firethroat |
|
72. |
Luscinia brunnea |
Indian Blue Robin |
|
73. |
Tarsiger chrysaeus |
Golden Bush-robin |
|
74. |
Tarsiger indicus |
White-browed Bush-robin |
|
75. |
Tarsiger hyperythrus |
Rufous-breasted Bush-robin |
|
76. |
Phoenicurus erythronota |
Rufous-backed Redstart |
|
77. |
Phoenicurus caeruleocephalus |
Blue-capped Redstart |
|
78. |
Phoenicurus schisticeps |
White-throated Redstart |
|
79. |
Hodgsonius phaenicuroides |
White-bellied Redstart |
|
80. |
Garrulax albogularis |
White-throated Laughingthrush |
|
81. |
Garrulax striatus |
Striated Laughingthrush |
|
82. |
Garrulax ocellatus |
Spotted Laughingthrush |
|
83. |
Garrulax lineatus |
Streaked Laughingthrush |
|
84. |
Garrulax subunicolor |
Scaly Laughingthrush |
|
85. |
Garrulax elliotii |
Elliot's Laughingthrush |
|
86. |
Garrulax variegatus |
Variegated Laughingthrush |
|
87. |
Garrulax affinis |
Black-faced Laughingthrush |
|
88. |
Xiphirhynchus superciliaris |
Slender-billed Scimitar-babbler |
|
89. |
Pnoepyga albiventer |
Greater Scaly-breasted Wren-babbler |
|
90. |
Spelaeornis troglodytoides |
Bar-winged Wren-babbler |
|
91. |
Spelaeornis formosus |
Spotted Wren-babbler |
|
92. |
Spelaeornis chocolatinus |
Long-tailed Wren-babbler |
|
93. |
Pteruthius xanthochlorus |
Green Shrike-babbler |
|
94. |
Minla strigula |
Chestnut-tailed Minla |
|
95. |
Minla ignotincta |
Red-tailed Minla |
|
96. |
Alcippe chrysotis |
Golden-breasted Fulvetta |
|
97. |
Alcippe vinipectus |
White-browed Fulvetta |
|
98. |
Heterophasia capistrata |
Rufous Sibia |
|
99. |
Yuhina gularis |
Stripe-throated Yuhina |
|
100. |
Yuhina occipitalis |
Rufous-vented Yuhina |
|
101. |
Myzornis pyrrhoura |
Myzornis |
|
102. |
Conostoma oemodium |
Great Parrotbill |
|
103. |
Paradoxornis unicolor |
Brown Parrotbill |
|
104. |
Paradoxornis fulvifrons |
Fulvous-fronted Parrotbill |
|
105. |
Tesia castaneocoronata |
Chestnut-headed Tesia |
|
106. |
Tesia cyaniventer |
Grey-bellied Tesia |
|
107. |
Cettia major |
Chestnut-crowned Bush-Warbler |
|
108. |
Cettia flavolivacea |
Aberrant Bush-Warbler |
|
109. |
Cettia acanthizoides |
Yellow-bellied Bush-Warbler |
|
110. |
Cettia brunnifrons |
Grey-sided Bush-Warbler |
|
111. |
Bradypterus major |
Long-billed Bush-Warbler |
|
112. |
Phylloscopus subaffinis |
Buff-throated Warbler |
|
113. |
Phylloscopus pulcher |
Orange-barred Leaf Warbler |
|
114. |
Phylloscopus maculipennis |
Grey-faced Leaf Warbler |
|
115. |
Phylloscopus magnirostris |
Large-billed Leaf-Warbler |
|
116. |
Phylloscopus occipitalis |
Western Crowned-Warbler |
|
117. |
Seicercus poliogenys |
Grey-cheeked Flycatcher Warbler |
|
118. |
Muscicapa ruficauda |
Rusty-tailed Flycatcher |
|
119. |
Muscicapa ferruginea |
Ferruginous Flycatcher |
|
120. |
Ficedula hodgsonii |
Rusty-breasted Blue Flycatcher |
|
121. |
Ficedula strophiata |
Orange-gorgeted Flycatcher |
|
122. |
Ficedula superciliaris |
Ultramarine Flycatcher |
|
123. |
Ficedula tricolor |
Slaty-blue Flycatcher |
|
124. |
Ficedula sapphira |
Sapphire Flycatcher |
|
125. |
Niltava sundara |
Rufous-bellied Niltava |
|
126. |
Aegithalos iouschistos |
Rufous-fronted Tit |
|
127. |
Cephalopyrus flammiceps |
Fire-capped Tit |
|
128. |
Parus rufonuchalis |
Rufous-naped Crested Tit |
|
129. |
Parus rubidiventris |
Rufous-bellied Crested Tit |
|
130. |
Parus melanolophus |
Spot-winged Crested Tit |
|
131. |
Parus dichrous |
Brown Crested Tit |
|
132. |
Parus monticolus |
Green-backed Tit |
|
133. |
Sylviparus modestus |
Yellow-browed Tit |
|
134. |
Sitta himalayensis |
White-tailed Nuthatch |
|
135. |
Sitta leucopsis |
White-cheeked Nuthatch |
|
136. |
Certhia himalayana |
Bar-tailed Tree-creeper |
|
137. |
Certhia nipalensis |
Rusty-flanked Tree-creeper |
|
138. |
Dicaeum melanoxanthum |
Yellow-bellied Flowerpecker |
|
139. |
Aethopyga ignicauda |
Fire-tailed Sunbird |
|
140. |
Serinus thibetanus |
Tibetan Siskin |
|
141. |
Carduelis spinoides |
Yellow-breasted Greenfinch |
|
142. |
Carduelis ambigua |
Black-headed Greenfinch |
|
143. |
Carpodacus rubescens |
Blanford's Rosefinch |
|
144. |
Carpodacus nipalensis |
Dark-breasted Rosefinch |
|
145. |
Carpodacus rodochrous |
Pink-browed Rosefinch |
|
146. |
Carpodacus vinaceus |
Vinaceous Rosefinch |
|
147. |
Carpodacus edwardsii |
Dark-rumped Rosefinch |
|
148. |
Carpodacus rodopeplus |
Spot-winged Rosefinch |
|
149. |
Carpodacus thura |
White-browed Rosefinch |
|
150. |
Pinicola subhimachalus |
Crimson-browed Finch |
|
151. |
Haematospiza sipahi |
Scarlet Finch |
|
152. |
Pyrrhula nipalensis |
Brown Bullfinch |
|
153. |
Pyrrhula erythrocephala |
Red-headed Bullfinch |
|
154. |
Pyrrhula erythaca |
Grey-headed Bullfinch |
|
155. |
Mycerobas icterioides |
Black-and-yellow Grosbeak |
|
156. |
Mycerobas affinis |
Collared Grosbeak |
|
157. |
Mycerobas melanozanthos |
Spotted-winged Grosbeak |
|
158. |
Mycerobas carnipes |
White-winged Grosbeak |
|
159. |
Pyrrhoplectes epauletta |
Gold-naped Finch |
|
160. |
Urocissa flavirostris |
Yellow-billed Blue Magpie |
BIOME 08: SINO-HIMALAYAN SUBTROPICAL FOREST
LOCATION: South-eastern China, Taiwan, the Himalayan foothills of Pakistan, India, Nepal and Bhutan, and the mountains of Bangladesh, Myanmar, Thailand, Laos, Cambodia, Vietnam and peninsular Malaysia. Mainly between c.1,000 and 2,000 m.
KEY HABITATS: Lower montane rain forest; Hill evergreen forest; Pine forest.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Chinese subtropical forests (EBA 140; 5 species); South-East Chinese mountains (EBA 141; 5 species); Hainan (EBA 142; 4 species); Da Lat plateau (EBA 145; 8 species); Taiwan (EBA 149; 15 species); Myanmar‑Thailand mountains (SA 080; 1 species); Doi Chiang Dao (SA 081; 1 species); Southern Laos (SA 083; 2 species); Kontum Plateau (SA 084; 3 species); Thailand‑Cambodia mountains (SA 085; 1 species).
NOTES: A few of the species of this biome range into the mountains of peninsular Malaysia, and there is therefore some overlap with the Sundaic montane forest (Biome 15). Note that the division of this biome from the Indochinese tropical moist forest (Biome 09) is particularly difficult, with some species listed for the two biomes overlapping in altitudinal range.
|
|
SPECIES |
ENGLISH |
|
161. |
Microhierax melanoleucus |
Pied Falconet |
|
162. |
Arborophila rufogularis |
Rufous-throated Hill-Partridge |
|
163. |
Bambusicola fytchii |
Mountain Bamboo-partridge |
|
164. |
Syrmaticus humiae |
Mrs. Hume's Pheasant |
|
165. |
Prozana bicolor |
Black-tailed Crake |
|
166. |
Psittacula himalayana |
Slaty-headed Parakeet |
|
167. |
Psittacula finschii |
Grey-headed Parakeet |
|
168. |
Chrysococcyx maculatus |
Asian Emerald Cuckoo |
|
169. |
Batrachostomus hodgsoni |
Hodgson's Frogmouth |
|
170. |
Alcedo hercules |
Great Blue Knigfisher |
|
171. |
Anorrhinus tickelli |
Brown Hornbill |
|
172. |
Aceros nipalensis |
Rufous-necked Hornbill |
|
173. |
Megalaima franklinii |
Golden-throated Barbet |
|
174. |
Megalaima asiatica |
Blue-throated Barbet |
|
175. |
Dendrocopos atratus |
Stripe-breasted Woodpecker |
|
176. |
Blythipicus pyrrhotis |
Bay Woodpecker |
|
177. |
Pitta nipalensis |
Blue-naped Pitta |
|
178. |
Coracina melaschistos |
Black-winged Cuckoo-shrike |
|
179. |
Pericrocotus roseus |
Rosy Minivet |
|
180. |
Pericrocotus brevirostris |
Short-billed Minivet |
|
181. |
Spizixos canifrons |
Crested Finchbill |
|
182. |
Pycnonotus striatus |
Striated Bulbul |
|
183. |
Pycnonotus leucogenys |
Himalayan Bulbul |
|
184. |
Pycnonotus flavescens |
Flavescent Bulbul |
|
185. |
Alophoixus flaveolus |
White-throated Bulbul |
|
186. |
Hypsipetes mcclellandii |
Rufous-bellied Bulbul |
|
187. |
Hypsipetes leucocephalus |
Black Bulbul |
|
188. |
Chloropsis hardwickii |
Orange-bellied Leafbird |
|
189. |
Lanius collurioides |
Burmese Shrike |
|
190. |
Monticola cinclorhynchus |
Blue-headed Rock-thrush |
|
191. |
Zoothera wardii |
Pied Thrush |
|
192. |
Zoothera marginata |
Lesser Long-billed Thrush |
|
193. |
Turdus unicolor |
Tickell's Thrush |
|
194. |
Turdus dissimilis |
Black-breasted Thrush |
|
195. |
Turdus boulboul |
Grey-winged Blackbird |
|
196. |
Cinclidium leucurum |
White-tailed Robin |
|
197. |
Cinclidium frontale |
Blue-fronted Robin |
|
198. |
Enicurus schistaceus |
Slaty-backed Forktail |
|
199. |
Cochoa purpurea |
Purple Cochoa |
|
200. |
Cochoa viridis |
Green Cochoa |
|
201. |
Garrulax galbanus |
Yellow-throated Laughingthrush |
|
202. |
Garrulax gularis |
Rufous-vented Laughingthrush |
|
203. |
Garrulax cineraceus |
Ashy Laughingthrush |
|
204. |
Garrulax rufogularis |
Rufous-chinned Laughingthrush |
|
205. |
Garrulax caerulatus |
Grey-sided Laughingthrush |
|
206. |
Garrulax merulinus |
Spot-breasted Laughingthrush |
|
207. |
Garrulax sannio |
White-browed Laughingthrush |
|
208. |
Garrulax squamatus |
Blue-winged Laughingthrush |
|
209. |
Liocichla phoenicea |
Red-faced Liocichla |
|
210. |
Pellorneum albiventre |
Spot-throated Babbler |
|
211. |
Pomatorhinus erythrocnemis |
Spot-breasted Scimitar-babbler |
|
212. |
Pomatorhinus erythrogenys |
Rusty-cheeked Scimitar-babbler |
|
213. |
Pomatorhinus ochraceiceps |
Loyd's or Longbilled Scimater Babbler |
|
214. |
Napothera brevicaudata |
Streaked Wren-babbler |
|
215. |
Stachyris ruficeps |
Rufous-capped Babbler |
|
216. |
Stachyris pyrrhops |
Black-chinned Babbler |
|
217. |
Babax lanceolatus |
Chinese Babax |
|
218. |
Leiothrix lutea |
Red-billed Leiothrix |
|
219. |
Cutia nipalensis |
Cutia |
|
220. |
Pteruthius rufiventer |
Rufous-bellied Shrike Babbler |
|
221. |
Gampsorhynchus rufulus |
White-hooded Babbler |
|
222. |
Actinodura egertoni |
Rusty-fronted Barwing |
|
223. |
Minla cyanouroptera |
Blue-winged Minla |
|
224. |
Alcippe cinerea |
Yellow-throated Fulvetta |
|
225. |
Alcippe cinereiceps |
Streak-throated Fulvetta |
|
226. |
Alcippe brunnea |
Dusky Fulvetta |
|
227. |
Alcippe nipalensis |
Nepal Fulvetta |
|
228. |
Heterophasia annectens |
Rufous-backed Sibia |
|
229. |
Yuhina castaniceps |
Striated Yuhina |
|
230. |
Yuhina nigrimenta |
Black-chinned Yuhina |
|
231. |
Paradoxornis gularis |
Grey-headed Parrotbill |
|
232. |
Paradoxornis guttaticollis |
Spot-breasted Parrotbill |
|
233. |
Paradoxornis atrosuperciliaris |
Lesser Rufous-headed Parrotbill |
|
234. |
Paradoxornis ruficeps |
Greater Rufous-headed Parrotbill |
|
235. |
Prinia criniger |
Brown Prinia |
|
236. |
Tesia olivea |
Slaty-bellied Tesia |
|
237. |
Cettia pallidipes |
Pale-footed Bush-Warbler |
|
238. |
Seicercus xanthoschistos |
Grey-headed Flycatcher Warbler |
|
239. |
Seicercus affinis |
White-spectacled Flycatcher Warbler |
|
240. |
Abroscopus albogularis |
Rufous-faced Flycatcher Warbler |
|
241. |
Abroscopus schisticeps |
Black-faced Flycatcher Warbler |
|
242. |
Muscicapa muttui |
Brown-breasted Flycatcher |
|
243. |
Ficedula monileger |
White-gorgeted Flycatcher |
|
244. |
Niltava macgrigoriae |
Small Niltava |
|
245. |
Aegithalos concinnus |
Red-headed Tit |
|
246. |
Parus spilonotus |
Black-spotted Yellow Tit |
|
247. |
Sitta formosa |
Beautiful Nuthatch |
|
248. |
Aethopyga saturata |
Black-throated Sunbird |
|
249. |
Arachnothera magna |
Streaked Spiderhunter |
|
250. |
Saroglossa spiloptera |
Spot-winged Starling |
|
251. |
Sturnus sinensis |
White-shouldered Starling |
|
252. |
Oriolus tenuirostris |
Slender-billed Oriole |
|
253. |
Oriolus traillii |
Maroon Oriole |
|
254. |
Garrulus lanceolatus |
Black-throated Jay |
|
255. |
Dendrocitta formosae |
Grey Treepie |
|
256. |
Dendrocitta frontalis |
Black-browed Treepie |
BIOME 09: INDOCHINESE TROPICAL MOIST FORESTS
LOCATION: Southern Nepal and Bhutan, Bangladesh, extreme southern China, Myanmar, Thailand, Laos, Cambodia and Vietnam. Mainly below c.1,000 m.
KEY HABITATS: Lowland evergreen rain forest; Semi-evergreen rain forest; Moist deciduous forest.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Annamese lowlands (EBA 143; 8 species); South Vietnamese lowlands (EBA 144; 3 species); North Myanmar lowlands (SA 079; 1 species).
|
|
SPECIES |
ENGLISH |
|
257. |
Ardea insignis |
White-bellied Heron |
|
258. |
Arborophila atrogularis |
White-cheeked Hill- Partridge |
|
259. |
Polyplectron bicalcaratum |
Grey Peacock-pheasant |
|
260. |
Heliopais personata |
Masked Finfoot |
|
261. |
Columba punicea |
Purple Wood Pigeon |
|
262. |
Dinopium shorii |
Himalayan Flameback |
|
263. |
Gecinulus grantia |
Pale-headed Woodpecker |
|
264. |
Pitta cyanea |
Blue Pitta |
|
265. |
Iole virescens |
Olive Bulbul |
|
266. |
Enicurus immaculatus |
Black-backed Forktail |
|
267. |
Garrulax monileger |
Lesser Necklaced Laughingthrush |
|
268. |
Garrulax pectoralis |
Greater Necklaced Laughingthrush |
|
269. |
Garrulax ruficollis |
Rufous-necked Laughingthrush |
|
270. |
Alcippe rufogularis |
Rufous-throated Fulvetta |
|
271. |
Prinia cinereocapilla |
Grey-crowned Prinia |
|
272. |
Cyornis poliogenys |
Brooks or Pale-chinned Flycatcher |
|
273. |
Melanochlora sultanea |
Sultan Tit |
|
274. |
Ampeliceps coronatus |
Gold-crested Myna |
|
275. |
Dicrurus annectans |
Crow-billed Drongo |
BIOME 10: INDIAN PENINSULA TROPICAL MOIST FOREST
LOCATION: The Western Ghats and isolated areas of moist forest in the Eastern Ghats and elsewhere in peninsular India, and the wet zone of Sri Lanka. Mainly below c.1,000 m.
KEY HABITATS: Lowland evergreen rain forest; Semi-evergreen rain forest; Moist deciduous forest; Hill evergreen forest.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Western Ghats (EBA 123; 16 species); Sri Lanka (EBA 124; 23 species); Central Indian forests (SA 075; 1 species).
|
|
SPECIES |
ENGLISH |
|
276. |
Phaenicophaeus viridirostris |
Small Green-billed Malkoha |
|
277. |
Batrachostomus moniliger |
Ceylon Frogmouth |
|
278. |
Caprimulgus atripennis |
Jerdon's Nightjar |
|
279. |
Collocalia unicolor |
Indian Edible-nest Swiftlet |
|
280. |
Harpactes fasciatus |
Malabar Trogon |
|
281. |
Anthracoceros coronatus |
Malabar Pied-hornbill |
|
282. |
Megalaima viridis |
White-cheeked Barbet |
|
283. |
Megalaima rubricapilla |
Crimson-throated Barbet |
|
284. |
Hirundo domicola |
Hill Swallow |
|
285. |
Iole indica |
Yellow-browed Bulbul |
|
286. |
Myiophonus horsfieldii |
Malabar Whistling-thrush |
|
287. |
Pomatorhinus horsfieldii |
Indian Scimitar-babbler |
|
288. |
Rhopocichla atriceps |
Black-headed Babbler |
|
289. |
Nectarinia lotenia |
Loten's Sunbird |
|
290. |
Lonchura kelaarti |
Black-throated Munia |
BIOME 11: INDO-MALAYAN TROPICAL DRY ZONE
LOCATION: Pakistan, India, Sri Lanka (dry zone), southern Nepal and Bhutan, Bangladesh, southern China, Myanmar, Thailand, Laos, Cambodia, Vietnam, Malaysia, Indonesia (Java only).
KEY HABITATS: Dry deciduous forest; Dry evergreen forest; Thorn forest; Semi-desert scrub; Wooded grassland; Secondary grassland; Arable land; Abandoned farmland.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Irrawaddy plains (EBA 132; 2 species); Eastern Andhra Pradesh (SA 071; 1 species); Southern Deccan Plateau (SA 072; 1 species).
NOTES: This biome includes a wide range of habitats, including both forests and open country. Many of the species listed have adapted to man-modified habitats, and these are given in angled brackets (i.e. species name). Some species have changed their distributions so much that they may not prove to be useful in identifying IBAs for the protection of this biome - these are given in double angled brackets (i.e. species name).
|
|
SPECIES |
ENGLISH |
|
291. |
Pseudibis papillosa |
Red-naped Ibis |
|
292. |
Gyps bengalensis |
White-rumped Vulture |
|
293. |
Gyps indicus |
Long-billed Vulture |
|
294. |
Sarcogyps calvus |
Red-headed Vulture |
|
295. |
Butastur teesa |
White-eyed Buzzard |
|
296. |
Falco chicquera |
Red-headed Falcon |
|
297. |
Francolinus pictus |
Painted Francolin |
|
298. |
Coturnix coromandelica |
Rain Quail |
|
299. |
Perdicula asiatica |
Jungle Bush-quail |
|
300. |
Perdicula argoondah |
Rock Bush-quail |
|
301. |
Perdicula erythrorhyncha |
Painted Bush-quail |
|
302. |
Galloperdix lunulata |
Painted Spurfowl |
|
303. |
Pavo cristatus |
Indian Peafowl |
|
304. |
Pavo muticus |
Green Peafowl |
|
305. |
Sypheotides indica |
Lesser Florican |
|
306. |
Vanellus malabaricus |
Yellow-wattled Lapwing |
|
307. |
Cursorius coromandelicus |
Indian Courser |
|
308. |
Treron phoenicoptera |
Yellow-legged Green-pigeon |
|
309. |
Psittacula cyanocephala |
Plum-headed Parakeet |
|
310. |
Psittacula roseata |
Blossom-headed Parakeet |
|
311. |
Phaenicophaeus leschenaultii |
Sirkeer Malkoha |
|
312. |
Bubo coromandus |
Dusky Eagle-owl |
|
313. |
Strix ocellata |
Mottled Wood-owl |
|
314. |
Caprimulgus asiaticus |
Common Indian Nightjar |
|
315. |
Ocyceros birostris |
Indian Grey-hornbill |
|
316. |
Megalaima zeylanica |
Brown-headed Barbet |
|
317. |
Megalaima lineata |
Lineated Barbet |
|
318. |
Dendrocopos mahrattensis |
Yellow-crowned Woodpecker |
|
319. |
Dinopium benghalense |
Black-rumped Flameback |
|
320. |
Chrysocolaptes festivus |
White-naped Woodpecker |
|
321. |
Mirafra erythroptera |
Red-winged Bush Lark |
|
322. |
Mirafra assamica |
Bengal Bush Lark |
|
323. |
Eremopterix grisea |
Ashy-crowned Sparrow-lark |
|
324. |
Calandrella raytal |
Indian Short-toed Lark |
|
325. |
Galerida malabarica |
Malabar Crested Lark |
|
326. |
Galerida deva |
Syke's Crested Lark |
|
327. |
Coracina melanoptera |
Black-headed Cuckoo-shrike |
|
328. |
Pericrocotus cinnamomeus |
Small Minivet |
|
329. |
Pericrocotus erythropygius |
White-bellied Minivet |
|
330. |
Tephrodornis pondicerianus |
Common Woodshrike |
|
331. |
Pycnonotus luteolus |
White-browed Bulbul |
|
332. |
Aegithina nigrolutea |
Marshall's Iora |
|
333. |
Saxicoloides fulicata |
Indian Robin |
|
334. |
Cercomela fusca |
Indian Chat |
|
335. |
Dumetia hyperythra |
Tawny-bellied Babbler |
|
336. |
Turdoides malcolm |
Large Grey Babbler |
|
337. |
Turdoides striatus |
Jungle Babbler |
|
338. |
Turdoides affinis |
White-headed Babbler |
|
339. |
Prinia buchanani |
Rufous-fronted Prinia |
|
340. |
Prinia sylvatica |
Jungle Prinia |
|
341. |
Prinia socialis |
Ashy Prinia |
|
342. |
Rhipidura aureola |
White-browed Fantail- Flycatcher |
|
343. |
Parus nuchalis |
Pied Tit |
|
344. |
Amandava formosa |
Green Munia |
|
345. |
Padda oryzivora |
Java Sparrow |
|
346. |
Sturnus malabaricus |
Grey-headed Starling |
|
347. |
Sturnus pagodarum |
Brahminy Starling |
|
348. |
Acridotheres ginginianus |
Bank Myna |
|
349. |
Dicrurus caerulescens |
White-bellied Drongo |
|
350. |
Artamus fuscus |
Ashy Woodswallow |
BIOME 12: INDO-GANGETIC PLAINS
LOCATION: Plains of Pakistan, northern India, southern Nepal and Bhutan, Bangladesh, extreme southern China, Myanmar, Thailand, Laos, Cambodia, Vietnam.
KEY HABITATS: Wetlands; Moist/marshy grassland; Scrub on marshy ground.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: Assam plains (EBA 131; 3 species); Indus plains (SA 074; 1 species).
|
|
SPECIES |
ENGLISH |
|
351. |
Francolinus gularis |
Swamp Francolin |
|
352. |
Houbaropsis bengalensis |
Bengal Florican |
|
353. |
Saxicola leucura |
White-tailed Stonechat |
|
354. |
Saxicola jerdoni |
Jerdon's Bushchat |
|
355. |
Chrysomma altirostre |
Jerdon's Babbler |
|
356. |
Turdoides earlei |
Striated Babbler |
|
357. |
Turdoides longirostris |
Slender-billed Babbler |
|
358. |
Prinia burnesii |
Rufous-vented Prinia |
|
359. |
Chaetornis striatus |
Bristled Grassbird |
|
360. |
Graminicola bengalensis |
Rufous-rumped Grassbird |
|
361. |
Ploceus benghalensis |
Black-breasted Weaver |
|
362. |
Ploceus megarhynchus |
Finn's Weaver |
|
363. |
Acridotheres albocinctus |
Collared Myna |
BIOME 13: SAHARO-SINDIAN DESERT
LOCATION: Pakistan and north-eastern India (extends through southern Iran to the Arabian Peninsula and North Africa).
KEY HABITATS: Desert dunes; Gravel and sand plains; Stone desert; Oases.
ENDEMIC BIRD AREAS AND SECONDARY AREAS: None.
|
|
SPECIES |
ENGLISH |
|
364. |
Ardeotis nigriceps |
Indian Bustard |
|
365. |
Pterocles senegallus |
Spotted Sandgrouse |
|
366. |
Caprimulgus mahrattensis |
Sykes's Nightjar |
|
367. |
Dendrocopos assimilis |
Sind Woodpecker |
|
368. |
Ammomanes deserti |
Desert Finch Lark |
|
369. |
Alaemon alaudipes |
Greater Hoopoe-lark |
|
370. |
Hirundo fuligula |
Pale Crag-martin |
|
371. |
Pycnonotus leucotis |
White-eared Bulbul |
|
372. |
Hypocolius ampelinus |
Hypocolius |
|
373. |
Saxicola macrorhyncha |
Stoliczka's Bushchat |
|
374. |
Rhodopechys githaginea |
Trumpeter Finch | |