1.
Status Of Wild Life Close To Indian Border Area At Ravi Siphon, Pakistan
by Muhammad Asif Munir | Dr. Zulfiqar Ali | Dr. Muhammad Mahmood-ul-Hassan.
Material type: ; Format:
print
Publisher: 2010Dissertation note: The proposed study was carried out at Ravi Siphon area in Sheikhupura district near Lahore, Punjab, which is an important site along the Indian Border. In this study, main emphasis was given on the population dynamics of birds, mammals, amphibians and reptiles in relation to the wetland characteristics particularly different types of riverine habitats, different seasons (summer, winter), relationship between different species of animals, seasonal changes, species identification, census of biodiversity and their population assessment. In addition, natural flora of the site was also recorded. Wildlife is an excellent indicator of the overall health of an ecosystem. On this research identification of nature and severity of problems being faced by biodiversity was identified and concluded as recommendation for the welfare of our wildlife to declare the site as a protected area.
Waterbirds depend on Ravi Siphon wetland for a variety of activities which include feeding, breeding, nesting and moulting. The highest number of waterbirds is often found in wetlands which have the greatest diversity of plant species and vegetation types, or where there is permanent water. In hot summer wetlands become visiting places for summer visitor birds and they provide a drought- refuge for several species of water birds.
During the study there were 87 species of birds recorded. According to seasonal distribution 24 winter visitors, 54 residents, 6 summer breeder and 3 year round visitor were recorded. In the study area, some birds were seen in a large diversity and others were seen rarely.
The present study about the status of bird species showed that 1 very common, 9 common, 20 fairly common, 34 uncommon, 12 rare and 11 very rare bird species were recorded. Monthly data was taken during the whole year (May 2009-April10) and 772 total birds population were found. In May 319, Jun 354, July 375, August 390, September 316, October 432, November 349, December 395, January 373. , February 389, March 401 and in April 363 bird's population were recorded.
Relative abundance, Census Index and Shannon Weiner Diversity Index were also calculated for studied bird data. The most dominant bird of the area was Indian Cliff Swallow found having relative abundance 5.69. The other dominant birds were Little Green Bee-eater (3.4), Large Egret (3.96), House Sparrow (2.3), and Bank Myna (2.6). Census Index was found to be 1.64 and Shannon Weiner Diversity Index was 5.98 found. Wildlife other than birds was also recorded. Three species of amphibians, eight species of reptiles and significant species of mammals were studied. A great variety of plant trees were also found at Ravi Siphon.
Availability: Items available for loan: UVAS Library [Call number: 1173,T] (1).
2.
Ecology And Population Of Birds Of Changa Manga Forest, Pakistan
by Irfan | Dr. Zulfiqar Ali | Dr. Muhammad Mahmood-ul-Hassan.
Material type: ; Format:
print
Publisher: 2010Dissertation note: The proposed study was carried out at Changa Manga that is an important woodland forest in Punjab. In this study, main emphasis was given on the population dynamics of birds in relation to the woodland characteristics particularly different types of forest habitats, different seasons (summer, winter), relationship between different species of birds, seasonal changes, species identification, census of birds and their population assessment. They connect all of us, from city dwellers to rural communities, to the environment. Birds are an excellent indicator of the overall health of an ecosystem. On this research identification of nature and severity of problems being faced by birds both resident and migratory was identified and concluded as recommendation for the welfare of our avifauna at the site.
In the site of study area resident birds are common and winter visitors, summer breeder birds were also recorded. In the study area 51 residents, 5 summer breeder, 21 winter visitor and 1 year round visitor species recorded. The total number of birds observed in Changa Manga Forest is 78 that show the most common birds in Changa Manga Forest are House Crow, Common Myna, Bank Myna, House Sparrow and Bee-eater etc.
The data collected from Changa Manga in May (524), June (384), July (544), August (418), September (425), October (487), November (647), December (593), January (532), February (604), March (630) and April (466).
The relative abundance is showed by house crow (7.8531). It is a garbage feeder so can easily be seen in areas which are the places of public interest, where people use to create or spread solid waste (wrapper, plastic bags, food material etc). Common Myna (4.4143), Bank Myna (4.3969), House sparrow (4.1641) and Blyth's Reed Warbler (3.1128), Small Sky-lark (2.3416), Common Babbler (2.6398), Blue-cheeked Bee-eater (2.0016), Small Sky Lark (2.3416), Long Tailed Grass Warbler (1.6631) and Indian Robin (1.6681) have abundance respectively. Census index (0.2422) and Shannon Wiener (5.5495) values were also calculated. The trophic levels were mention according to these; there were 263 birds' herbivores, 411 were omnivores, 391 were insectivores and 112 were carnivore's birds in the study area.
Hence there is a strong need to restore, conserve and preserve these existing woodland to maintain and improve the distribution, diversity and abundance of populations and habitats of breeding, migratory and nonbreeding birds throughout the land forests of the Pakistan
Availability: Items available for loan: UVAS Library [Call number: 1174,T] (1).
3.
Ecology And Diversity Of Head Qadirabad, Gujranwala, Punjab, Pakistan
by Muhammad Altaf | Dr. Zulfiqar Ali | Dr. Muhammad Mahmood-ul-Hassan.
Material type: ; Format:
print
Publisher: 2010Dissertation note: The proposed study was carried out at Head Qadirabad that was an important wetland of the Punjab. In this study, main emphasis was given on the ecology and diversity of waterbirds in relation to the wetland characteristics particularly different types of aquatic habitats, different seasons, relationship between different species of waterbirds, seasonal changes, species identification, census of waterbirds and their population assessment. They connect all of us, from city dwellers to rural communities, to the environment. Migratory birds were an excellent indicator of the overall health of an ecosystem. On this research identification of nature and severity of problems being faced by waterbirds both resident and migratory was identified and concluded as recommendation for the welfare of our avifauna at the site.
The lower basin of the Chenab River was a prime example of the consequences and challenges posed by increasing water scarcity. The aim of this study was Development, Environment, and Security and the water birds and to clarify key concepts and criteria for sustainable water use within the Head Qadirabad, and then, using those criteria, to present patterns of water use, allocation, and management that can continue to support economic prosperity while maintaining ecological integrity.
Water is a prerequisite for life, and a key ingredient in virtually all human economic activity. In regions where demands for water approach or exceed the limits of available supplies, competition intensifies among various interests turning water scarcity into a potential source of conflict. Scarcity often also results in unhealthy aquatic ecosystems because of alterations in the timing, quantity, and quality of freshwater flows needed to sustain their natural functions. This ecological degradation, in turn, spawns a variety of undesirable economic and social effects.
In the study area observed 76 winter visitor species, 54 resident species, 10 summer breeder species and 9 year round visitor species (Table: 4.3 and Figure: 4.2.)
House Crow was much dominant (Relative abundance was 3.6585), Little Green Bee eater (Relative abundance was 3.2520), Little Swift (Relative abundance was 2.8455), House Sparrow (Relative abundance was 2.5203), Bank Myna (Relative abundance was 2.0325), Common Myna (Relative abundance was 2.0325), Black Kite (Relative abundance was 2.0325), Cattle Egret (Relative abundance was 1.7886), Red-wattled Lapwing (Relative abundance was 1.6260) and Small Pied kingfisher (Relative abundance was 1.2195). These were all dominant in the Head Qadirabad area. This all data shown in Table: 4.9 and Figure: 4.4.
In the present study observed following number of birds in whole year, in May 354, Jun 388, July 388, August 404, September 361, October 341, November 394, December 344, January 560, February 649, March 591 and in April 593 birds, as present in Table: 4.10 and Figure 4.5.
The present study showed that, 149 species of birds were present in the study area. In 2009- 10 observed that Census Index was 0.437 and Shanon-Weiner Diversity Index was 9.58 as shown in Table: 4.12.
Availability: Items available for loan: UVAS Library [Call number: 1178,T] (1).
4.
Urbanization: Consequences On Increase Of Garbage Eating Birs In Lahore, Pakistan
by Muhammad tanveer | Dr. Zulfiqar Ali | Dr. Ali Nawaz | Prof. Dr. Nureen Aziz.
Material type: ; Format:
print
Publisher: 2010Dissertation note: This proposed study was analyzed the increase of garbage eating birds in Lahore. Five Important sites were selected in Lahore as whole longitudinal belt of Lahore was covered. Many birds species were recorded, and especially garbage eating or scavenger birds' population was observed and its consequences on other birds species and ecosystem was studied. Different field observation methods for birds along with field guides was adopted. In this 12 month study, month wise record of birds was depicted a picture of population of birds in Lahore. The vultures were totally extinct in Lahore and were not observed at any sites. During the study observed most of the birds were the resident, few were winter visitor and very low numbers were the summer breeders. Urbanization is a major cause of habitat loss and fragmentation. According to present study density of birds were recorded at Jinnah garden, Racecourse Park, Woodland Safari Park, Mehmood Booti and Old Ravi Bridge. Different threats to the birds were also been recorded and appropriate conservation measure towards a sustainable ecosystem was proposed.
Availability: Items available for loan: UVAS Library [Call number: 1181,T] (1).
5.
Habitat, Morphology And General Biology Of Bats Of Fmaily Embellonuridae
by Sana Ashraf | Dr. Muhammad Mahmood ul Hassan | Dr. Zulfiqar Ali | Prof. Dr.Masroor.
Material type: ; Format:
print
Publisher: 2010Dissertation note: The present study was designed to investigate habitat, morphology and general biology of the bats belonging to family Embellonuridae from Punjab. A total of fifteen specimens of sheath- tailed bats belonging to two species were captured from Attock and Bahawalpur districts and identified. These included eleven specimens of the naked-rumped tomb bat (Taphozous nudiventris) and four specimens of Egyptian tomb bat (T. perforates). The later species is a new record from the present study area.
A roost of sheath-tailed bats was located with help of some locals in the suburbs of the Ratowal village in Attock district from where four naked-rumped tomb bats (T. nudiventris) were captured with the help of hand net. Acacia catechu, A. nilotica, A. modesta, Bauhinia variegate, Olea ferruginea, Phylianthus emblica and Quercus leucotrichophora were the main tree species present in the area while the shrubs included Carissa opaca, Calotropis procera, Dodonaea viscose, Justica adhatoda and Otostegia limbata. A ilium jaquemontii, Arundo donax, Cannabis sativa, Centaurea iberica, Eulophia dabia, Geranium oceiiatum and Hibiscus caesius, were some notable herb species in that habitat.
Approximately three hundred bats were roosting on the walls and ceiling of the shrine located in the vicinity of Mojgarh from where five bats were captured. Two of these were Egyptian tomb bats (T. perforatus) while the remaining three were naked-rumped tomb bats (T. nudiventris). Six hundred and thirty five bats were counted on the walls and ceilings of various rooms of the ruined Derawar Fort of which six bats were captured. One of these was T perforatus while the remainings were T. nudiventris.
The mean body weight of the eleven T. nudiventris was 48.7 g ± 11.63 (SD) while their head and body length was 87.9 mm ± 6.20 (SD). Free tail, ear and tragus were 17.3 mm ± 3.38 (SD), 13.9 mm± 2.21 (SD) and 4.1 mm ± 0.54 (SD) long, respectively. The forearm was 70.5 mm ± 0.93 (SD) long. Thumb and claw were 7.8 mm ± 0.84 (SD) and 2.5 ± 0.35 (SD) long respectively. The mean length of 3', 4th and 5th metacarpals was 62.3 mm ± 2.54 (SD), 50.6 mm ± 2.28 (SD) and 38.2 mm ± 9.78 (SD), respectively. The 1st and 2'' phalanges of 3rd metacarpal
27.3 mm ± 1.03 (SD) and 28.6 mm ± 2.40 (SD) long, respectively while the same on 4th metacarpal were 13.6 mm ± 2.63 (SD) and 8.3 mm ± 1.03 (SD) long, respectively. Their wingspan was 36.6 mm ± 3.28 (SD). Hind foot, tibia and calcar were 14.8 mm ± 1.40 (SD), 29.0 mm ± 1.10 (SD) and 5.6 mm ± 1.91 (SD) long, respectively while male had a 5.8 mm ± 1.39 (SD) long penis.
A total of four specimens of the Egyptian tomb bat were collected from Bhawalpur district at Mojgarh (n = 2), Derawar fort (n= 1), and Rattowal (n= 1) from Attock district in the areas of Punjab. The mean body weight of these specimens was 37.6 g ± 15.07 (SD). Their mean head and body, free tail and ear length was 82.0 mm ± 4.40 (SD), 21.0 mm ± 2.16 (SD) and 15.0 mm ± 3.16 (SD), respectively. The mean length of tragus was 4.0 mm ± 0.00 (SD). Length of the forearm was 63.8 mm ± 1.50 (SD). Length of thumb and of claw was 8.0 mm ± 0.71 (SD) and 2.8 ± 0.29 (SD). The mean length of 3rd metacarpal , 1st phalanx on 3fd metacarpal and 2' phalanx on 3ft metacarpal were 59.6 mm ± 6.57 (SD), 25.1 mm ± 1.65 (SD) and 27.4mm ±2.43 (SD) respectively. The mean length of 4th maetacarpal and it's 1st and 2nd halanx were 47.0 mm ± 2.86 (SD), 13.4mm±1.60 (SD) and 7.8mm ± 2.25 (SD), respectively. The4 mean length of 5th metacarpal was 40.8 mm± 6.99(SD) Their wingspan was 30.9mm ±1.80 (SD). Hind foot and tiabia length was 15.5mm ± 1.29 (SD). Their calcar and penis length was 6.0mm ±1.41 (SD) and 5.9 mm± 1.93 (SD) respectively.
Availability: Items available for loan: UVAS Library [Call number: 1195,T] (1).
6.
Comunity Druven Sustainable Management Of Natural Resources Of Taunsa Barrage Wildlife Sanctuaty,
by Fehmeeda Bibi | Dr. Zulfiqar Ali.
Material type: ; Format:
print
; Literary form:
not fiction
Publisher: 2012Dissertation note: Abstract Availability: Items available for loan: UVAS Library [Call number: 1496,T] (1).
7.
Bats (Chiroptera: Mammalia) Of Malakand Division, Pakistan
by Mohammad Salim (2007-VA-543) | Dr. Arshad Javid | Dr. Muhammad Sajid Nadeem | Dr. Zulfiqar Ali | Prof. Dr. Azhar Maqbool.
Material type: ; Literary form:
not fiction
Publisher: 2016Dissertation note: The present study was conducted from 2010 to 2013 in three districts (Malakand, Dir and Swat) of Malakand Division. A total of 49 stations were sampled for bats where total 1982 bats were recorded. A total of 21 species of bats belonging to six families, fourteen genera were recorded. These includes the Indian flying fox (Pteropus giganteus), the greater short-nosed fruit bat (Cynopterus sphinx), the fulvous fruit bat (Rousettus leschenaultia), the greater mouse-tailed bat (Rhinopoma microphyllum), the lesser mouse tailed bat (Rhinopoma hardwickii), the greater false vampire (Megaderma lyra), the greater horseshoe bat (Rhinolophus ferrumequinum), the Blyth‟s horseshoe bat (Rhinolophus Lepidus), the fulvous leaf-nosed bat (Hipposideros fulvus), the Hodgson‟s bat (Myotis formosus), the Asian barbastelle (Barbastella leucomelas), the Asiatic greater yellow house bat (Scotophilus heathii), the Asiatic lesser yellow house bat (Scotophilus kuhlii), the serotine (Eptesicus serotinus), the common pipistrelle (Pipistrellus pipistrellus), the javan pipistrelle (Pipistrellus javanicus), the coromandel pipistrelle (Pipistrellus coromandra), the least pipistrelle (Pipistrellus tenuis), the Dormer‟s bat (Pipistrellus dormeri), the desert yellow bat (Scotoecus pallidus) and the Schreiber‟s long-fingered bat (Miniopterus fuliginosus) were recorded throughout the study area.
M. formosus was common to all the three districts while B. leucomelas and P. pipistrellus were captured only from Dir district. The Hodgson‟s bat (M. formosus) and the Schreiber‟s long-fingered bat (M. fuliginosus) were captured from Malakand and Swat districts. The skeleton of C. sphinx was recorded only from adjacent area of Malakand district. The Indian flying fox (Pteropus giganteus) was not previously recorded from Khyber Pakhtunkhwa while it has been reported from Punjab and Sindh province of the country. There are only six species which has
Summary
181
previously been reported from Khyber Pakhtunkhwa while thirteen bats were newly recorded from the study area. Only two bats were newly recorded for the first time in the country.
The mean forearm length of the three P. giganteus was 152.23 mm ± 3.72 (SD). The mean greatest skull length was 65.96 mm ± 1.42 (SD). The maxillary toothrow length was 24.91 mm ± 0.84 (SD). The mandible and mandibular toothrow length were 50.78 mm ± 0.87 (SD) and 27.41 mm ± 0.66 (SD), respectively.
The thumb and forearm length of one C. sphinx was 25.80 mm and 65.48 mm, respectively. The greatest length of skull was 32.20 mm. The maxillary and mandibular toothrow length were 10.86 mm and 12.64 mm. The mandible was 24.75 mm long.
The mean forearm and thumb of R. leschenaultii was 80.23 mm ± 3.26 (SD) and 27.79 mm ± 1.22 (SD), long, respectively. The mean greatest skull length was 36.97 mm ± 1.11 (SD). The mean mandible, maxillary and mandibular toothrow length were 28.95 mm ± 0.90 (SD), 14.08 mm ± 0.44 (SD) and 15.51 mm ± 0.47 (SD), respectively.
Mean thumb and forearm length of three R. microphyllum was 8.80 mm ± 0.95 (SD) and 67.45 mm ± 4.60 (SD), respectively. The mean greatest length of skull was 20.15 mm ± 0.64 (SD). The mandible, maxillary and mandibular toothrow length were 7.30 mm ± 0.18 (SD), 8.11 mm ± 0.11 (SD) and 14.38 mm ± 0.63 (SD), respectively.
Mean thumb and forearm length of R. hardwickii was 8.23 mm ± 0.38 (SD) and 59.90 mm ± 1.21 (SD), respectively. The mean greatest length of skull of the four specimens was 18.20 mm ± 0.48 (SD). The maxillary and mandibular toothrow length were 6.08 mm ± 0.07 (SD) and 6.72 mm ± 0.13 (SD), respectively. The mandible length was measured as 12.38 mm ± 0.0.23 (SD).
Mean thumb and forearm length of M. lyra was 11.80 mm ± 0.44 (SD) and 70.06 mm ± 0.69 (SD), respectively. Mean greatest length of skull of the three specimens was 29.60 mm ± 0.46
Summary
182
(SD). The maxillary toothrow length was 11.40 mm ± 0.10 (SD). The mandibular toothrow length was 11.94 mm ± 0.04 (SD). The mandible length was measured as 20.04 mm ± 0.03 (SD).
Mean thumb and forearm length of R. ferrumequinum was 4.01 mm ± 0.01 (SD) and 60.01 mm ± 1.41 (SD), respectively. The mean greatest length of skull of the two specimens was 23.35 mm ± 0.20 (SD). The maxillary toothrow length was 9.18 mm ± 0.02 (SD). The mandibular toothrow length was 9.86 mm ± 0.01 (SD). The mandible length was measured as 16.33 mm ± 0.13 (SD).
The mean thumb and forearm length of R. lepidus was 3.87 mm ±0.13 (SD) and 38.02 mm ± 0.63 (SD), respectively. The mean greatest length of skull of the two specimens was 15.94 mm ± 0.15 (SD). The maxillary toothrow length was 5.86 mm ± 0.02 (SD). The mandibular toothrow length was 6.57 mm ± 0.64 (SD). The mandible length was measured as 10.34 mm ± 0.04 (SD).
Mean thumb and forearm length of H. fulvus was 4.91 mm ± 0.17 (SD) and 41.41 mm ± 0.97 (SD), respectively. The mean greatest length of skull of the thirteen specimens was 18.45 mm ± 0.16 (SD). The maxillary toothrow length was 6.50 mm ± 0.14 (SD). The mandibular toothrow length was 6.96 mm ± 0.18 (SD). The mandible length was measured as 11.73 mm ± 0.14 (SD).
Mean thumb and forearm length of M. formosus was 9.26 mm ± 0.70 (SD) and 48.74 mm ± 2.02 (SD), respectively. The mean greatest length of skull of the three specimens was 17.81 mm ± 0.12 (SD). The maxillary toothrow length was 7.15 mm ± 0.05 (SD). The mandibular toothrow length was 7.80 mm ± 0.05 (SD). The mandible length was measured as 13.85 mm ± 0.07 (SD).
Thumb and forearm length of B. leucomelas was 5.65 mm and 42.88 mm, respectively. The tragus height was 10.32 mm. The greatest length of skull of a single specimen was 15.87 mm. The maxillary toothrow length was 4.91 mm. The mandibular toothrow length was 5.43 mm. The mandible length was measured as 10.02 mm.
Summary
183
Mean thumb and forearm length of S. heathii was 9.06 mm ± 0.41 (SD) and 62.25 mm ± 1.76 (SD), respectively. The mean greatest length of skull of the nine specimens was 23.12 mm ± 0.46 (SD). The maxillary toothrow length was 7.87 mm ± 0.16 (SD). The mandibular toothrow length was 8.93 mm ± 0.16 (SD). The mandible length was measured as 16.62 mm ± 0.19 (SD).
Mean thumb and forearm length of S. kuhlii was 7.01 mm ± 1.41 (SD) and 50.06 mm ± 7.13 (SD), respectively. The mean greatest length of skull of the two specimens was 19.24 mm ± 0.71 (SD). The maxillary toothrow length was 6.49 mm ± 0.11 (SD). The mandibular toothrow length was 7.42 mm ± 0.01 (SD). The mandible length was measured as 13.78 mm ± 0.47 (SD).
Mean thumb and forearm length of E. serotinus was 8.92 mm ± 0.32 (SD) and 53.37 mm ± 1.39 (SD), respectively. The mean greatest length of skull of the fifteen specimens was 21.40 mm ± 0.70 (SD). The maxillary toothrow length was 7.84 mm ± 0.21 (SD). The mandibular toothrow length was 9.28 mm ± 1.95 (SD). The mandible length was measured as 15.51 mm ± 1.94 (SD).
Thumb and forearm length of P. pipistrellus was 4.01 mm and 31.06 mm, respectively. The greatest length of skull of a single specimen was 12.14 mm. The maxillary toothrow length was 4.22 mm. The mandibular toothrow length was 4.45 mm. The mandible length was measured as 8.27 mm.
Thumb and forearm length of P. javanicus was 4.02 mm and 32.01 mm, respectively. The greatest length of skull of a single specimen was 13.13 mm. The maxillary toothrow length was 4.60 mm. The mandibular toothrow length was 5.20 mm. The mandible length was measured as 9.46 mm.
Mean thumb and forearm length of P. coromandra was 4.70 mm ± 0.45 (SD) and 32.28 mm ± 1.17 (SD), respectively. The mean greatest length of skull of the eight specimens was 12.67 mm
Summary
184
± 0.40 (SD). The maxillary toothrow length was 4.44 mm ± 0.24 (SD). The mandibular toothrow length was 4.74 mm ± 0.23 (SD). The mandible length was measured as 9.13 mm ± 0.46 (SD).
Mean thumb and forearm length of P. tenuis was 4.43 mm ± 0.47 (SD) and 29.24 mm ± 1.03 (SD), respectively. The mean greatest length of skull of the 23 specimens was 11.56 mm ± 0.25 (SD). The maxillary toothrow length was 3.87 mm ± 0.09 (SD). The mandibular toothrow length was 4.10 mm ± 0.06 (SD). The mandible length was measured as 7.89 mm ± 0.60 (SD).
Mean thumb and forearm length of P. dormeri was 5.28 mm ± 0.70 (SD) and 34.30 mm ± 1.25 (SD), respectively. The mean greatest length of the skull was 13.77 mm ± 0.11 (SD). The mandible, maxillary and mandibular toothrow length were measured as 10.53 mm ± 0.09 (SD), 5.33 mm ± 0.02 (SD) and 5.56 mm ± 0.07 (SD), respectively.
Mean thumb and forearm length of S. pallidus was 6.26 mm ± 0.41 (SD) and 36.83 mm ± 0.42 (SD), respectively. The mean greatest length of skull of the twenty two specimens was 15.00 mm ± 0.26 (SD). The maxillary toothrow length was 5.66 mm ± 0.10 (SD). The mandible and mandibular toothrow length were 11.35 mm ± 0.23 (SD) and 6.11 mm ± 0.12 (SD), respectively.
Mean thumb and forearm length of M. fuliginosus bat was 6.61 mm ± 0.43 (SD) and 37.59 mm ± 5.37 (SD), respectively. The mean greatest length of skull of the six specimens was 14.48 mm ± 0.58 (SD). The maxillary toothrow length was 5.32 mm ± 0.39 (SD). The mandible and mandibular toothrow length were 10.54 mm ± 0.65 (SD) and 5.71 mm ± 0.49 (SD), respectively.
FUTURE RECOMMENDATIONS
1. Bat surveys. This is the first extensive exploration of that small portion of the Khyber Pakhtunkhwa which comprises of only three districts of Malakand Division i.e. Malakand, Dir and Swat. Although more focus remained towards Malakand district, six families, fourteen genera, twenty one species were identified. Moreover, two new country
Summary
185
records (Myotis formosus and Miniopterus fuliginosis) were also explored. Further bat surveys in poorly surveyed parts of the country especially in KPK and Baluchistan may result in identification of some other new bat taxa. More bat surveys involving greater field efforts may also confirm the presence or absence of those already described from the country.
2. Distribution ranges and species specific habitat analysis. Presence of thirteen new locality records (Pteropus giganteus, Cynopterus sphinx, Rhinopoma hardwickii, Megaderma lyra, Rhinolophus Lepidus, Hipposideros fulvus, Barbastella leucomelas, Scotophilus heathii, Scotophilus kuhlii, Eptesicus serotinus, Pipistrellus javanicus, Pipistrellus dormeri and Scotoecus pallidus) and two new country records (Myotis formosus and Miniopterus fuliginosis) gives credence to the idea that distribution ranges of most of the bat species has change over the past sixty years. Thus serious scientific studies are needed to redefine distribution ranges and identify species specific habitats using global positioning system and radio-telemetric studies.
3. Reconfirmation of bat taxonomy. Genetic analysis of none of the bat species of the country has been made using molecular markers thus leaving behind a chance to doubt identification of cryptic bat species. Thus molecular genetic studies of all the bat species of the country is highly recommended which may also lead to the discovery of such bat taxa which are new to science.
4. Bat call library. The only bat detector (Patterson D 1000X) present in the country fell down from my hand in a water body and became out of order. So none of the bat could be recorded. Bat call analysis has boosted bat identification throughout the world but the
Summary
186
lack of such sophisticated equipment in the country has become a major bottle neck in the establishment of a bat call library.
5. Awareness campaigns. Majority of the countrymen are unaware of the ecological services rendered by bats. Khyber Pakhtunkhwa is the major fruit growing region of the country. Based on misperceptions, the locals consider all bats as vermin and kill them ruthlessly. Conservation education to highlight the significance of bats must be included in the curriculum of children at primary school level so that they may adopt a pro-conservation attitude in the first few years of their personality building. Availability: Items available for loan: UVAS Library [Call number: 2610-T] (1).
