# Avian Diversity and Abundance of Taunsa Barrage Ramsar Site in Punjab, Pakistan

Authors: Muhammad Zeshan Haider; Shakeel Ahmed; Nuzhat Sial; Gulnaz Afzal; Ayesha Riaz; Akhtar Rasool Asif; Tahir Mehmood; Abdul Rasheed; Sayyed Aun Muhammad; Hafiz Ishfaq Ahmad
Journal: Journal of Zoological Systematics and Evolutionary Research
 (2022)

---

## Abstract

The study of avian species diversity and abundance at the Taunsa Barrage Ramsar site was carried out from September 2019 to March 2020. Taunsa Barrage is an important wetland for international and local migratory birds, including waterfowls, waders, and long-distance migrant avifauna. Data were collected by direct counts made on four-point transects representing a disturbance gradient due to humans and different habitats. Species diversity indices, analysis of variance (ANOVA), and other statistical methods were used to analyze data. A total of 150 avian species of 19 orders and 53 families were recorded. These included 66 migrant species and 84 resident species. The spotting of ten globally threatened species also highlights the importance of wetland for avian species. On average,1511±373 (mean±SD) species of birds were recorded every month. Shannon’s diversity index indicated that Transect Point 2 had higher species diversity (H′=3.779), followed by Transect Points 3, 4, and 1 (H′=3.769, H′=3.491, and H′=3.457, respectively). Evenness index showed that birds evenly distributed in September (E=0.5584) than November (E=0.3109). ANOVA showed a significant difference (F=4.800, df=3, P=0.002) of avian diversity and abundance among the transect points. But there was no statistically significant interaction between months (F=1.23, df=6, P=0.233). The results showed that the Taunsa Barrage Ramsar site harbors plenty of resident migratory and threatened bird species. Hence, it is important to protect its habitat and need to protect avian diversity by overcoming major threats.


---

## Body

## 1. Introduction

Birds are a key component of the world’s ecosystems [1]. Wild birds are present worldwide, from pole habitats to the equator habitats [2]. They are essential for continuing ecological circles, particularly in the food chain ranging from consumers to top predators [3]. They are extremely vulnerable to climate change, and even minor temperature changes disturb their distribution and diversity [4]. Therefore, their diversity plays a vital role as environmental indicators in evaluating the quality of habitats and the state of our natural world [5]. In 1958, Taunsa Barrage was built to maintain a discharge of up to 1,000,000 cusecs on an Indus River [6]. First time at upstream of the barrage, the wildlife sanctuary was established in 1972 of 65.6 km2 area [7].Variable climate patterns in Pakistan result in diverse wetlands and classified into different wetlands. Wetlands serve as a transitional area between land-based and water ecosystems where water-levels are normally at or close to the land’s surface [8]. Wetland habitats are important for biodiversity genetic variations and evolution [9]. Bird communities are a vital part of the wetland ecosystems. Wetland habitats provide vital wintering, staging, and breeding sites for various water birds [10]. Bird diversity and abundance depend on wetland characteristics such as food availability, water quality, wintering, and breeding grounds [11]. Wetland provides a suitable habitat for biodiversity like birds, mammals, amphibians, fish, reptiles, and plants [12]. Therefore, wetlands are distinctive biological communities supporting plant and animal diversity [13].Species diversity and abundance are equally key factors for improving the ecosystem [14]. Patterns of avian diversity and composition are the outcomes of evolutionary, historical, and environmental processes [15]. Assessment of bird communities has become a useful tool in biodiversity conservation and finding measures for the conservation of high human pressure areas [16]. However, monitoring the abundance of bird species provides useful information, widely used in bird conservation and management of threatened and endangered species [17]. Moreover, seasonal bird monitoring is equally important to finding dynamic bird movement in specific habitats [18].Biodiversity monitoring at the Ramsar site provides valuable information on biodiversity, wetland quality, and economic importance. This information can develop wetland policies and conservation strategies [19]. Wetland avifauna species are virtuous ecological pointers indicating the condition of wetlands, and these are the source of unifying factors among countries through migration around the world. Birds are useful environmental indicators, helping us find important places and can provide a useful sign of how well the country’s ecosystems offer benefits to people. Thus, ornithological research and monitoring of wetland biodiversity are essential ecological tools that provide valuable information for sustainable environments and climate change worldwide [20].The study was planned to observe species diversity and abundance of wild birds at Taunsa Barrage (a Ramsar site). The avifauna of the Taunsa Barrage Ramsar site has been studied earlier by several researchers (Akbar et al. [21–25]). The authors have already reported a preliminary systematic checklist of 171 bird species found in TBWS [26]. Despite these works, a few areas of the Ramsar site were unattended; therefore, the present study was undertaken. This study comes with further additions and information on the relative abundance and seasonal status of migratory birds, focusing on raptors’ diversity and distribution status. The purpose of this study was to identify the current diversity of birds, major threats, and threatened bird species. However, the assessment of bird population status and trends from the Taunsa Barrage Ramsar site deserves the utmost significance for bird conservation. This study also carries great importance for wetland management and bird conservation, especially the migratory birds.


## 2. Materials and Methods

### 2.1. Study Area

Taunsa Barrage (a Ramsar site) is located on the Indus River in south-western Punjab. Geographically, it is situated between 30°30′46″ North latitudes and 70°50′57″ East longitudes, with an altitude of 139 m (Figure 1). The area is Tehsil Kot Addu of Pakistan’s District Muzaffargarh, Punjab province. It takes its name from a city called Taunsa Sharif, located about 30 km from the barrage. Taunsa Barrage was built over five years (1953-1958) on the River Indus. It was declared a Wildlife Sanctuary in 1978 with 6,576 hectares. In 1996, Taunsa Barrage was designated as a Ramsar site covering 16,000 hectares [27, 28]. Taunsa barrage wildlife sanctuary (TBWS) was renotified in 2004 with an extended area (Akbar et al. [21]). The sanctuary area covers 9 km upstream and 3 km downstream from the barrage [29].Figure 1
Map showing location of Taunsa Barrage Ramsar site and selected study sites for monitoring avian species.This wetland provides a suitable habitat for biodiversity, including plants, birds, mammals, fishes, amphibians, and reptiles. This site is linked to the Indus flyway and provides an ambient environment for migratory bird survival. The Wildlife Sanctuary supports a rich variety of wildlife, including 253 avian species, 5 large mammals, 21 small mammals, 3 amphibians, 17 reptiles, and 67 fish species (Akbar et al. [21]). The sanctuary is also rich in plant species, with 120 species having been documented [30]. The study area qualifies as an Important Bird and Key Biodiversity Area because it owns a globally threatened species [31]. Threatened species like the Hog Deer, Indus Dolphin, Smooth-coated Indian Otter, Marbled Teal, and Pond Spotted Turtle. Taunsa Barrage Ramsar site is also an important breeding location for water birds such as Pheasant-tailed Jacana, Lesser Whistling-Duck, and Ruddy Crake (Akbar et al. [21]). The area supports a variety of bird species and provides critical breeding, staging, and wintering grounds for various water birds [23].Its climate is arid with particularly hot summer seasons and mild winters. The average lowest temperature is between 5 and 6°C in January, while extreme is between 41 and 43°C in June. Annual rainfall average is between 150 and 400 mm and relative humidity of 25-85%. Wind speed stays at 15-30 km/h and shoots up to 30-35 km/h with dust storms and haze during summer. Wind direction is from north to south or northwest to southeast [28].


### 2.2. Methods

The fieldwork (from Sep-2019 to Mar-2020) was based on the direct observation method [32]. Point transect sampling was selected to count and record all birds seen or heard and birds in flight. A total of four-point transects were made to study the diversity and abundance of birds (see Table 1). Locations of these transects were selected to cover all wetland habitats (see Figure 1). Bird surveys were carried out between early mornings (30 min after dawn) and until three hours after sunrise [33]. Bird count data was taken in two sessions. The first session was from early morning to 9 or 10 AM when bird activity declined. The second session was from mid-day or from 4 to 6 PM, as this is the period when most raptors and other birds are active.Table 1
Details of study sites selected for surveying birds of Taunsa Barrage Ramsar site.
Transect NameCoordinates at startCoordinates at endLength (km)DescriptionTP.130.51012 N30.49578 N1.5 kmBasti Faqir Wali, fruit gardens, crops cultivated land, & high human disturbance70.83167 E70.82864 ETP.230.51871 N30.51277 N1.5 kmFishponds, crops cultivation area, & low human disturbance70.84099 E70.82479 ETP.330.51735 N30.52997 N1.5 kmBund tract, crops cultivation area during dry season, wintering area for water birds, lotus growing area, & very low human disturbance70.85597 E70.86243 ETP.430.51992 N30.53320 N1.5 kmLeft Marginal Bund (LMB), wintering area for water birds, crops cultivation area, & medium human disturbance70.87608 E70.87644 EAll the surveys were conducted by foot. Point transects during the morning and evenings were considered by individual surveys. Binoculars of ZEISS,10×42 were used to observe the birds. GPS map 62 was used to record the coordinates of transects and species location. A Nikon D90 (70-300 mm lens) camera was used to take the birds’ photos. Birds were identified by using field guides ([34]: [35–41]). The status of residential, migratory, terrestrial, and water birds was assessed with the help of field guides. Photos of the birds taken from field surveys were identified and verified by the field guides.


### 2.3. Data Analysis

All the collected field work data of birds were processed using MS excel 365. MS excel 365 was used to calculate individuals’ mean values, standard deviation, and standard error values. PAST version 2.17C software [42] analyzed diversity indices (Dominance, Simpson, Shannon, and Evenness) and Bray-Curtis cluster analysis. The maximum count of individuals was taken per month and transect, from September 2019 until March 2020. The mean number of avian species and individuals recorded during the study period from four study sites was compared using One-Way ANOVA.


## 2.1. Study Area

Taunsa Barrage (a Ramsar site) is located on the Indus River in south-western Punjab. Geographically, it is situated between 30°30′46″ North latitudes and 70°50′57″ East longitudes, with an altitude of 139 m (Figure 1). The area is Tehsil Kot Addu of Pakistan’s District Muzaffargarh, Punjab province. It takes its name from a city called Taunsa Sharif, located about 30 km from the barrage. Taunsa Barrage was built over five years (1953-1958) on the River Indus. It was declared a Wildlife Sanctuary in 1978 with 6,576 hectares. In 1996, Taunsa Barrage was designated as a Ramsar site covering 16,000 hectares [27, 28]. Taunsa barrage wildlife sanctuary (TBWS) was renotified in 2004 with an extended area (Akbar et al. [21]). The sanctuary area covers 9 km upstream and 3 km downstream from the barrage [29].Figure 1
Map showing location of Taunsa Barrage Ramsar site and selected study sites for monitoring avian species.This wetland provides a suitable habitat for biodiversity, including plants, birds, mammals, fishes, amphibians, and reptiles. This site is linked to the Indus flyway and provides an ambient environment for migratory bird survival. The Wildlife Sanctuary supports a rich variety of wildlife, including 253 avian species, 5 large mammals, 21 small mammals, 3 amphibians, 17 reptiles, and 67 fish species (Akbar et al. [21]). The sanctuary is also rich in plant species, with 120 species having been documented [30]. The study area qualifies as an Important Bird and Key Biodiversity Area because it owns a globally threatened species [31]. Threatened species like the Hog Deer, Indus Dolphin, Smooth-coated Indian Otter, Marbled Teal, and Pond Spotted Turtle. Taunsa Barrage Ramsar site is also an important breeding location for water birds such as Pheasant-tailed Jacana, Lesser Whistling-Duck, and Ruddy Crake (Akbar et al. [21]). The area supports a variety of bird species and provides critical breeding, staging, and wintering grounds for various water birds [23].Its climate is arid with particularly hot summer seasons and mild winters. The average lowest temperature is between 5 and 6°C in January, while extreme is between 41 and 43°C in June. Annual rainfall average is between 150 and 400 mm and relative humidity of 25-85%. Wind speed stays at 15-30 km/h and shoots up to 30-35 km/h with dust storms and haze during summer. Wind direction is from north to south or northwest to southeast [28].


## 2.2. Methods

The fieldwork (from Sep-2019 to Mar-2020) was based on the direct observation method [32]. Point transect sampling was selected to count and record all birds seen or heard and birds in flight. A total of four-point transects were made to study the diversity and abundance of birds (see Table 1). Locations of these transects were selected to cover all wetland habitats (see Figure 1). Bird surveys were carried out between early mornings (30 min after dawn) and until three hours after sunrise [33]. Bird count data was taken in two sessions. The first session was from early morning to 9 or 10 AM when bird activity declined. The second session was from mid-day or from 4 to 6 PM, as this is the period when most raptors and other birds are active.Table 1
Details of study sites selected for surveying birds of Taunsa Barrage Ramsar site.
Transect NameCoordinates at startCoordinates at endLength (km)DescriptionTP.130.51012 N30.49578 N1.5 kmBasti Faqir Wali, fruit gardens, crops cultivated land, & high human disturbance70.83167 E70.82864 ETP.230.51871 N30.51277 N1.5 kmFishponds, crops cultivation area, & low human disturbance70.84099 E70.82479 ETP.330.51735 N30.52997 N1.5 kmBund tract, crops cultivation area during dry season, wintering area for water birds, lotus growing area, & very low human disturbance70.85597 E70.86243 ETP.430.51992 N30.53320 N1.5 kmLeft Marginal Bund (LMB), wintering area for water birds, crops cultivation area, & medium human disturbance70.87608 E70.87644 EAll the surveys were conducted by foot. Point transects during the morning and evenings were considered by individual surveys. Binoculars of ZEISS,10×42 were used to observe the birds. GPS map 62 was used to record the coordinates of transects and species location. A Nikon D90 (70-300 mm lens) camera was used to take the birds’ photos. Birds were identified by using field guides ([34]: [35–41]). The status of residential, migratory, terrestrial, and water birds was assessed with the help of field guides. Photos of the birds taken from field surveys were identified and verified by the field guides.


## 2.3. Data Analysis

All the collected field work data of birds were processed using MS excel 365. MS excel 365 was used to calculate individuals’ mean values, standard deviation, and standard error values. PAST version 2.17C software [42] analyzed diversity indices (Dominance, Simpson, Shannon, and Evenness) and Bray-Curtis cluster analysis. The maximum count of individuals was taken per month and transect, from September 2019 until March 2020. The mean number of avian species and individuals recorded during the study period from four study sites was compared using One-Way ANOVA.


## 3. Results

### 3.1. Bird Monitoring Frequency

A total of 62 surveys were conducted from September 2019 to March 2020 to monitor bird diversity and abundance at four transects. Maximum surveys (14) were conducted in September, while the minimum (6) in March. The four study sites were selected to evaluate bird abundance; maximum surveys (21) were undertaken at Transect Points 1 and 2 while the minimum (6) at Transect Point 4. The study sites were monitored based on the weekly schedule. Under fieldwork plan, some surveys were not conducted due to weather conditions. Because of weather conditions, monitoring frequency was reduced to 6 visits at Transect Point 4.


### 3.2. Bird Species Composition

A total of 150 avian species of 19 orders and 53 families were recorded during Sep-2019 to Mar-2020. Order Passeriformes has the highest diversity (57 species from 23 families), followed by Charadriiformes (21 species from 6 families), Accipitriformes (14 species from 2 families), Anseriformes (12 species from single-family), Pelecaniformes (11 species from 2 families), Coraciiformes (5 species from 3 families), Piciformes, Gruiformes, and Suliformes (4 species from 2 families), Columbiformes (4 species from single-family), Cuculiformes and Falconiformes (3 species from single-family), Strigiformes (2 species from single-family), Podicipediformes, Galliformes, Psittaciformes, Phoenicopteriformes, Bucerotiformes, and Caprimulgiformes one species from single-family. Accipitridae, Ardeidae, and Anatidae were the leading families represented by 13, 11, and 10 species at the family level, respectively. Families Accipitridae (9%), Anatidae (8%), and Ardeidae (7%) had the largest number of bird species, while families Alaudidae (1.33%) and Recurvirostridae (0.66%) had the smallest number of bird species.At the species level, little cormorant (Microcarbo niger), common starling (Sturnus vulgaris), common myna (Acridotheres tristis), house crow (Corvus splendens), sind sparrow (Passer pyrrhonotus), cattle egret (Bubulcus ibis), black kite (Milvus migrans), and common pochard (Aythya ferina) had the highest number of individuals during the study period. Few species were recorded only in a single month during the study period, and some rare species (few in numbers) were recorded. Barred buttonquail (Turnix suscitator), pied cuckoo (Clamator jacobinus), steppe eagle (Aquila nipalensis), peregrine falcon (Falco peregrinus), and short-toed eagle (Circaetus gallicus) were observed only once throughout the study period. Out of the total avian species, 56% species were residents, 29% winter visitors, 4% winter migrants, 3% passage migrants, 3% summer breeding visitors, 2% double passage migrants, and 1% species summer migrants, occasional wintering, and breeding visitors (Figure 2).Figure 2
Percentage composition of species occurring in study area according to seasonal distribution status.


### 3.3. Bird Species Abundance

The maximum number of individual birds’N=10845 (including unknown species) with an average abundance of 1549±410mean±SD were recorded from September 2019 to March 2020. A total of 10575 individual birds representing 150 known avian species were recorded. The average abundance (mean±SD) of 150 bird species was 1511±373 (mean±SD) during the study period. Month-wise variation in average bird abundance was high during the November month with 1874 (24±58) and least during the February month with 1024 (15±28). Species richness was high during the October month (n=100) and least during the February month (n=67). The total average bird species richness was 80±11.95mean±SD during the study period.Avian species diversity and abundance in the area was typically dispersed among the four transects. Transect wise variation in the average bird abundance was high at Transect Point 3 with 5782 (826±144) and least at Transect Point 1 with 3927 (561±82). Species richness was high at Transect Point 3 (108) and least at Transect Point 1 (74). The average species richness (mean±SD) was high at Transect Point 2 with 52.28±3.85 and least at Transect Point 4 with 38.83±2.16.The average number of birds and species was varied between all transects. At Transect Point 1, the average number of birds and species was561±43.14 (mean±SD), and at the other three transects, it was 783.57±52.28, 826±44.28, and 809.83±38.83, respectively, (Figure 3). Based on species richness, Transect Point 2 was found to be dominant with 45 families and 18 orders, followed by the Transect Point 3 with 42 families and 17 orders, Transect Point 1 with 40 families and 16 orders, and less Transect Point 4 with 37 families and 14 orders.Figure 3
Monthly average number of bird species and individuals showing the highest values at Transect Points 2 and 3 recorded during Sep-2019 to Mar-2020.


### 3.4. Avian Diversity

The species diversity index fluctuated fromH′=3.989 (October) to H′=3.189 (November). The Shannon-Weiner diversity index revealed that the highest diversity of birds was observed during October month (H′=3.989), followed by the September, December, January, February, March, and November, i.e., 3.95, 3.68, 3.50, 3.41, 3.45, and 3.18, respectively, (Figure 4). The highest species evenness of birds was observed during September (eH/S=0.55), while the lowest was during the November month (eH/S=0.31). The Shannon-Weiner diversity index revealed that the highest diversity of birds was observed at Transect Point 2 (H′=3.779), followed by the Transect Points 3, 4, and 1, i.e., 3.769, 3.491, and 3.457, respectively (Figure 5). Based on the diversity, species evenness has shown variation among transects with values of 0.4285 (TP 1), 0.4129 (TP 2), 0.401 (TP 3), and 0.390 (TP 4). The Simpson index (1-D) revealed 0.954, 0.964, 0.960, and 0.94 for Transect Points 1, 2, 3, and 4, respectively, suggesting that Transect Points 2 and 3 had the highest avian species diversity (Tables 2 and 3).Figure 4
Monthly variations in species diversity indices from Sep-2019 to Mar-2020.Figure 5
Transect-wise variations in species diversity indices during Sep-2019 to Mar-2020.Table 2
Month-wise species abundance, richness, and species diversity indices from Sep-2019 to Mar-2020.
MonthNo. of speciesNo. of individualsDominance (D)Simpson (1-D)Shannon (H′)Evenness (eH/S)MargalefSeptember9319580.02740.97263.950.558412.14October10017850.027450.97253.9890.540213.18November7818300.090290.90973.1890.310910.25December7411790.03430.96573.6880.539910.32January7616040.049870.95013.5020.436810.16February6710240.065130.93493.4120.45269.522March7211950.055170.94483.4580.441110.02Grand total150105750.029320.97074.080.394515.99Table 3
Transect-wise species abundance, richness, and species diversity indices during Sep-2019 to Mar-2020.
Diversity indicesTransect Point 1Transect Point 2Transect Point 3Transect Point 4TotalNo. of species7410610884150No. of individuals392653365665470219629Dominance (D)0.045460.035310.039630.056650.03349Simpson (1-D)0.95450.96470.96040.94340.9665Shannon (H′)3.4573.7793.7693.4913.919Evenness (eH/S)0.42850.41290.40110.39080.3356Brillouin3.4143.7343.7253.453.899Menhinick1.1811.4511.4351.2251.071Margalef8.82112.2312.389.81615.07Equitability_J0.80310.81030.80490.7880.7821Fisher_alpha12.9418.7518.9314.5322.09Berger-Parker0.10490.090330.12710.18080.09567Chao-178.2109.3113.684.55153.5


### 3.5. Globally Threatened Species

A total of 150 bird species consisting of 140 Least Concern and 10 species were found to globally threatened and near threatened in the study area. According to the IUCN Red List 2021-3, six species Ferruginous Duck (Aythya nyroca), Eurasian Curlew (Numenius arquata), Northern Lapwing (Vanellus vanellus), River Tern (Sterna aurantia), Oriental Darter (Anhinga melanogaster), and Rufous-vented Prinia (Prinia burnesii) were identified as Near Threatened (NT). In contrast, Common Pochard (Aythya ferina) and Greater Spotted Eagle (Aquila clanga) were recognized as Vulnerable (VU) and Black-bellied Tern (Sterna acuticauda) and Steppe Eagle (Aquila nipalensis) as Endangered (E) species (Figures 6–9) (Table 4).Figure 6
Sterna acuticauda (EN), breeding adult, January 2020 (photo by Muhammad Zeshan Haider).Figure 7
Sterna aurantia (NT), breeding adult, January 2020 (photo by Muhammad Zeshan Haider).Figure 8
Aquila clanga (VU), immature, December 2019 (photo by Muhammad Zeshan Haider).Figure 9
Aquila nipalensis (EN), immature, January 2020 (photo by Muhammad Zeshan Haider).Table 4
List of globally threatened species recorded from Taunsa Barrage Ramsar site from Sep-2019 to Mar-2020.
S. no.Common nameScientific nameIUCN status1Common pochardAythya ferinaVU2Ferruginous duckAythya nyrocaNT3Eurasian curlewNumenius arquataNT4Northern lapwingVanellus vanellusNT5River ternSterna aurantiaNT6Black-bellied ternSterna acuticaudaEN7Greater spotted eagleAquila clangaVU8Steppe eagleAquila nipalensisEN9Oriental darterAnhinga melanogasterNT10Rufous-vented priniaPrinia burnesiiNT


### 3.6. Analysis of Variance (One-Way ANOVA)

The month-wise analysis (One-way ANOVA) did not yield any significant (p<0.05) differences in bird diversity among months from September 2019 to March 2020 (df=6, F=1.34, p=0.233). Although species composition contrasted between the months during the study period, significant differences were not found between months and years. Year-wise analysis showed that the difference was not statistically significant (df=1, F=2.51, and p=0.11). However, the analysis showed a nonsignificant interaction between year and month. The transect-wise analysis of variance showed that avian diversity varies significantly (p<0.05) across the four transects (Figure 10). The analysis revealed significant differences (F=4.800, df=3, p=0.002) in bird diversity across four different transects during the study period. Cluster analysis (Figure 11) shows the avian similarity of the four study sites in which TP3 and TP4 formed the first clade, which means that these transects shared mostly the same avifaunal species. These transects (3 and 4) have the highest similarity percentage, 72.5%. TP1 and TP2 habitats are less related to TP3 and TP4, with a percentage similarity of 60%.Figure 10
Transect-wise analysis of variance.Figure 11
Transect Bray-Curtis cluster analysis.


## 3.1. Bird Monitoring Frequency

A total of 62 surveys were conducted from September 2019 to March 2020 to monitor bird diversity and abundance at four transects. Maximum surveys (14) were conducted in September, while the minimum (6) in March. The four study sites were selected to evaluate bird abundance; maximum surveys (21) were undertaken at Transect Points 1 and 2 while the minimum (6) at Transect Point 4. The study sites were monitored based on the weekly schedule. Under fieldwork plan, some surveys were not conducted due to weather conditions. Because of weather conditions, monitoring frequency was reduced to 6 visits at Transect Point 4.


## 3.2. Bird Species Composition

A total of 150 avian species of 19 orders and 53 families were recorded during Sep-2019 to Mar-2020. Order Passeriformes has the highest diversity (57 species from 23 families), followed by Charadriiformes (21 species from 6 families), Accipitriformes (14 species from 2 families), Anseriformes (12 species from single-family), Pelecaniformes (11 species from 2 families), Coraciiformes (5 species from 3 families), Piciformes, Gruiformes, and Suliformes (4 species from 2 families), Columbiformes (4 species from single-family), Cuculiformes and Falconiformes (3 species from single-family), Strigiformes (2 species from single-family), Podicipediformes, Galliformes, Psittaciformes, Phoenicopteriformes, Bucerotiformes, and Caprimulgiformes one species from single-family. Accipitridae, Ardeidae, and Anatidae were the leading families represented by 13, 11, and 10 species at the family level, respectively. Families Accipitridae (9%), Anatidae (8%), and Ardeidae (7%) had the largest number of bird species, while families Alaudidae (1.33%) and Recurvirostridae (0.66%) had the smallest number of bird species.At the species level, little cormorant (Microcarbo niger), common starling (Sturnus vulgaris), common myna (Acridotheres tristis), house crow (Corvus splendens), sind sparrow (Passer pyrrhonotus), cattle egret (Bubulcus ibis), black kite (Milvus migrans), and common pochard (Aythya ferina) had the highest number of individuals during the study period. Few species were recorded only in a single month during the study period, and some rare species (few in numbers) were recorded. Barred buttonquail (Turnix suscitator), pied cuckoo (Clamator jacobinus), steppe eagle (Aquila nipalensis), peregrine falcon (Falco peregrinus), and short-toed eagle (Circaetus gallicus) were observed only once throughout the study period. Out of the total avian species, 56% species were residents, 29% winter visitors, 4% winter migrants, 3% passage migrants, 3% summer breeding visitors, 2% double passage migrants, and 1% species summer migrants, occasional wintering, and breeding visitors (Figure 2).Figure 2
Percentage composition of species occurring in study area according to seasonal distribution status.


## 3.3. Bird Species Abundance

The maximum number of individual birds’N=10845 (including unknown species) with an average abundance of 1549±410mean±SD were recorded from September 2019 to March 2020. A total of 10575 individual birds representing 150 known avian species were recorded. The average abundance (mean±SD) of 150 bird species was 1511±373 (mean±SD) during the study period. Month-wise variation in average bird abundance was high during the November month with 1874 (24±58) and least during the February month with 1024 (15±28). Species richness was high during the October month (n=100) and least during the February month (n=67). The total average bird species richness was 80±11.95mean±SD during the study period.Avian species diversity and abundance in the area was typically dispersed among the four transects. Transect wise variation in the average bird abundance was high at Transect Point 3 with 5782 (826±144) and least at Transect Point 1 with 3927 (561±82). Species richness was high at Transect Point 3 (108) and least at Transect Point 1 (74). The average species richness (mean±SD) was high at Transect Point 2 with 52.28±3.85 and least at Transect Point 4 with 38.83±2.16.The average number of birds and species was varied between all transects. At Transect Point 1, the average number of birds and species was561±43.14 (mean±SD), and at the other three transects, it was 783.57±52.28, 826±44.28, and 809.83±38.83, respectively, (Figure 3). Based on species richness, Transect Point 2 was found to be dominant with 45 families and 18 orders, followed by the Transect Point 3 with 42 families and 17 orders, Transect Point 1 with 40 families and 16 orders, and less Transect Point 4 with 37 families and 14 orders.Figure 3
Monthly average number of bird species and individuals showing the highest values at Transect Points 2 and 3 recorded during Sep-2019 to Mar-2020.


## 3.4. Avian Diversity

The species diversity index fluctuated fromH′=3.989 (October) to H′=3.189 (November). The Shannon-Weiner diversity index revealed that the highest diversity of birds was observed during October month (H′=3.989), followed by the September, December, January, February, March, and November, i.e., 3.95, 3.68, 3.50, 3.41, 3.45, and 3.18, respectively, (Figure 4). The highest species evenness of birds was observed during September (eH/S=0.55), while the lowest was during the November month (eH/S=0.31). The Shannon-Weiner diversity index revealed that the highest diversity of birds was observed at Transect Point 2 (H′=3.779), followed by the Transect Points 3, 4, and 1, i.e., 3.769, 3.491, and 3.457, respectively (Figure 5). Based on the diversity, species evenness has shown variation among transects with values of 0.4285 (TP 1), 0.4129 (TP 2), 0.401 (TP 3), and 0.390 (TP 4). The Simpson index (1-D) revealed 0.954, 0.964, 0.960, and 0.94 for Transect Points 1, 2, 3, and 4, respectively, suggesting that Transect Points 2 and 3 had the highest avian species diversity (Tables 2 and 3).Figure 4
Monthly variations in species diversity indices from Sep-2019 to Mar-2020.Figure 5
Transect-wise variations in species diversity indices during Sep-2019 to Mar-2020.Table 2
Month-wise species abundance, richness, and species diversity indices from Sep-2019 to Mar-2020.
MonthNo. of speciesNo. of individualsDominance (D)Simpson (1-D)Shannon (H′)Evenness (eH/S)MargalefSeptember9319580.02740.97263.950.558412.14October10017850.027450.97253.9890.540213.18November7818300.090290.90973.1890.310910.25December7411790.03430.96573.6880.539910.32January7616040.049870.95013.5020.436810.16February6710240.065130.93493.4120.45269.522March7211950.055170.94483.4580.441110.02Grand total150105750.029320.97074.080.394515.99Table 3
Transect-wise species abundance, richness, and species diversity indices during Sep-2019 to Mar-2020.
Diversity indicesTransect Point 1Transect Point 2Transect Point 3Transect Point 4TotalNo. of species7410610884150No. of individuals392653365665470219629Dominance (D)0.045460.035310.039630.056650.03349Simpson (1-D)0.95450.96470.96040.94340.9665Shannon (H′)3.4573.7793.7693.4913.919Evenness (eH/S)0.42850.41290.40110.39080.3356Brillouin3.4143.7343.7253.453.899Menhinick1.1811.4511.4351.2251.071Margalef8.82112.2312.389.81615.07Equitability_J0.80310.81030.80490.7880.7821Fisher_alpha12.9418.7518.9314.5322.09Berger-Parker0.10490.090330.12710.18080.09567Chao-178.2109.3113.684.55153.5


## 3.5. Globally Threatened Species

A total of 150 bird species consisting of 140 Least Concern and 10 species were found to globally threatened and near threatened in the study area. According to the IUCN Red List 2021-3, six species Ferruginous Duck (Aythya nyroca), Eurasian Curlew (Numenius arquata), Northern Lapwing (Vanellus vanellus), River Tern (Sterna aurantia), Oriental Darter (Anhinga melanogaster), and Rufous-vented Prinia (Prinia burnesii) were identified as Near Threatened (NT). In contrast, Common Pochard (Aythya ferina) and Greater Spotted Eagle (Aquila clanga) were recognized as Vulnerable (VU) and Black-bellied Tern (Sterna acuticauda) and Steppe Eagle (Aquila nipalensis) as Endangered (E) species (Figures 6–9) (Table 4).Figure 6
Sterna acuticauda (EN), breeding adult, January 2020 (photo by Muhammad Zeshan Haider).Figure 7
Sterna aurantia (NT), breeding adult, January 2020 (photo by Muhammad Zeshan Haider).Figure 8
Aquila clanga (VU), immature, December 2019 (photo by Muhammad Zeshan Haider).Figure 9
Aquila nipalensis (EN), immature, January 2020 (photo by Muhammad Zeshan Haider).Table 4
List of globally threatened species recorded from Taunsa Barrage Ramsar site from Sep-2019 to Mar-2020.
S. no.Common nameScientific nameIUCN status1Common pochardAythya ferinaVU2Ferruginous duckAythya nyrocaNT3Eurasian curlewNumenius arquataNT4Northern lapwingVanellus vanellusNT5River ternSterna aurantiaNT6Black-bellied ternSterna acuticaudaEN7Greater spotted eagleAquila clangaVU8Steppe eagleAquila nipalensisEN9Oriental darterAnhinga melanogasterNT10Rufous-vented priniaPrinia burnesiiNT


## 3.6. Analysis of Variance (One-Way ANOVA)

The month-wise analysis (One-way ANOVA) did not yield any significant (p<0.05) differences in bird diversity among months from September 2019 to March 2020 (df=6, F=1.34, p=0.233). Although species composition contrasted between the months during the study period, significant differences were not found between months and years. Year-wise analysis showed that the difference was not statistically significant (df=1, F=2.51, and p=0.11). However, the analysis showed a nonsignificant interaction between year and month. The transect-wise analysis of variance showed that avian diversity varies significantly (p<0.05) across the four transects (Figure 10). The analysis revealed significant differences (F=4.800, df=3, p=0.002) in bird diversity across four different transects during the study period. Cluster analysis (Figure 11) shows the avian similarity of the four study sites in which TP3 and TP4 formed the first clade, which means that these transects shared mostly the same avifaunal species. These transects (3 and 4) have the highest similarity percentage, 72.5%. TP1 and TP2 habitats are less related to TP3 and TP4, with a percentage similarity of 60%.Figure 10
Transect-wise analysis of variance.Figure 11
Transect Bray-Curtis cluster analysis.


## 4. Discussion

The present study was conducted to monitor bird diversity and abundance at Taunsa Barrage Ramsar site. Species richness and abundance has been the aim of many birds monitoring studies [43–45]. During the current study, 150 avian species of 19 orders and 53 families were observed (see Table 5). Biodiversity monitoring at the Ramsar site provides valuable information on biodiversity, wetland quality, and economic importance. This information can be used to develop wetland policies and conservation strategies [19]. Our results showed that Taunsa Barrage is an important wetland harboring a rich diversity of avian species. The study revealed that Taunsa Barrage Ramsar site is rich in avifaunal diversity as the value of the Shannon index ranges from 3.18 to 3.98, which is also supported by Bibi [26]; Bibi and Ali [24]. Our results are consistent with the other studies conducted for diversity and abundance [46–48].Table 5
Checklist of birds of Taunsa Barrage Ramsar site.
S. no.Order nameFamily nameCommon nameScientific nameIUCNstatusSeasonal status1GalliformesPhasianidaeGrey francolinFrancolinus pondicerianusLCR2CharadriiformesTurnicidaeBarred buttonquailTurnix suscitatorLCR3AnseriformesAnatidaeGreylag gooseAnser anserLCWM4Ruddy shelduckTadorna ferrugineaLCWM5GadwallAnas streperaLCWV6Eurasian wigeonAnas penelopeLCWV7MallardAnas platyrhynchosLCWV8Common tealAnas creccaLCWV9GarganeyAnas querquedulaLCSPM/APM10Northern pintailAnas acutaLCWV11Northern shovelerAnas clypeataLCWV12Common pochardAythya ferinaVUWV13Ferruginous duckAythya nyrocaNTWV14Tufted duckAythya fuligulaLCWV15PiciformesPicidaeEurasian wryneckJynx torquillaLCWV16Yellow-crowned woodpeckerDendrocopos mahrattensisLCR17Black-rumped flamebackDinopium benghalenseLCR18MegalaimidaeCoppersmith barbetMegalaima haemacephalaLCR19BucerotiformesUpupidaeCommon hoopoeUpupa epopsLCR20CoraciiformesCoraciidaeIndian rollerCoracias benghalensisLCR21AlcedinidaeCommon kingfisherAlcedo atthisLCR22White-throated kingfisherHalcyon smyrnensisLCR23Pied kingfisherCeryle rudisLCR24MeropidaeGreen bee-eaterMerops orientalisLCR25CuculiformesCuculidaePied cuckooClamator jacobinusLCBV26Asian koelEudynamys scolopaceusLCSM27Greater coucalCentropus sinensisLCR28PsittaciformesPsittaculidaeRose-ringed parakeetPsittacula krameriLCR29CaprimulgiformesApodidaeLittle swiftApus affinisLCR30StrigiformesStrigidaeIndian scops owlOtus bakkamoenaLCR31Spotted owletAthene bramaLCR32ColumbiformesColumbidaeRock pigeonColumba liviaLCR/WM33Laughing doveStreptopelia senegalensisLCR34Red collared doveStreptopelia tranquebaricaLCSBV35Eurasian collared doveStreptopelia decaoctoLCR36GruiformesGruidaeDemoiselle craneAnthropoides virgoLCAPM37RallidaeCommon moorhenGallinula chloropusLCR38White-breasted waterhenAmaurornis phoenicurusLCR39Common cootFulica atraLCWV40CharadriiformesScolopacidaeCommon snipeGallinago gallinagoLCWV41Eurasian curlewNumenius arquataNTWV42Common redshankTringa totanusLCWV43Common greenshankTringa nebulariaLCWV44Green sandpiperTringa ochropusLCWV45Common sandpiperActitis hypoleucosLCWV46Little stintCalidris minutaLCWV47Temminck’s stintCalidris temminckiiLCWV48JacanidaePheasant-tailed jacanaHydrophasianus chirurgusLCSBV49CharadriidaeLittle ringed ploverCharadrius dubiusLCWV50Northern lapwingVanellus vanellusNTWV51Red-wattled lapwingVanellus indicusLCR52White-tailed lapwingVanellus leucurusLCWV53Black-headed gullLarus ridibundusLCWV54LaridaeCaspian ternHydroprogne caspiaLCR55River ternSterna aurantiaNTR56Little ternSternula albifronsLCSBV57Black-bellied ternSterna acuticaudaENR58Whiskered ternChlidonias hybridaLCSPM/APM59RecurvirostridaeBlack-winged stiltHimantopus himantopusLCR60AccipitriformesPandionidaeOspreyPandion haliaetusLCWV61AccipitridaeBlack-winged kiteElanus caeruleusLCR62Black kiteMilvus migransLCR63Brahminy kiteHaliastur indusLCR64Short-toed snake eagleCircaetus gallicusLCR65Eurasian marsh-harrierCircus aeruginosusLCWV66ShikraAccipiter badiusLCR67Eurasian sparrowhawkAccipiter nisusLCWV68Oriental honey-buzzardPernis ptilorhynchusLCWV69White-eyed buzzardButastur teesaLCR70Common buzzardButeo buteoLCWV71Long-legged buzzardButeo rufinusLCWV72Greater spotted eagleAquila ClangaVUWV73Steppe eagleAquila nipalensisENWV74FalconiformesFalconidaeCommon kestrelFalco tinnunculusLCWV75Eurasian hobbyFalco subbuteoLCWV76Peregrine falconFalco peregrinusLCWV77PodicipediformesPodicipedidaeLittle grebeTachybaptus ruficollisLCR78SuliformesAnhingidaeOriental darterAnhinga melanogasterNTR79PhalacrocoracidaeLittle cormorantMicrocarbo nigerLCR80Indian cormorantPhalacrocorax fuscicollisLCR81Great cormorantPhalacrocorax carboLCR82PelecaniformesArdeidaeLittle egretEgretta garzettaLCR83Grey heronArdea cinereaLCWV84Purple heronArdea purpureaLCR85Great egretCasmerodius albusLCR86Intermediate egretMesophoyx intermediaLCR87Cattle egretBubulcus ibisLCR88Indian pond-heronArdeola grayiiLCR89Black-crowned night-heronNycticorax nycticoraxLCR90Cinnamon bitternIxobrychus cinnamomeusLCR91Great bitternBotaurus stellarisLCWM92ThreskiornithidaeEurasian spoonbillPlatalea leucorodiaLCWM93PhoenicopteriformesPhoenicopteridaeGreater flamingoPhoenicopterus roseusLCR94PasseriformesPasseriformesLaniidaeIsabelline shrikeLanius isabellinusLCWM95Bay-backed shrikeLanius vittatusLCR96Long-tailed shrikeLanius schachLCR97CorvidaeRufous treepieDendrocitta vagabundaLCR98House crowCorvus splendensLCR99OriolidaeEurasian golden orioleOriolus oriolusLCPM100DicruridaeBlack drongoDicrurus macrocercusLCR101VangidaeCommon woodshrikeTephrodornis pondicerianusLCR102TurdidaeBlack-throated thrushTurdus atrogularisLCWM103MuscicapidaeRed-breasted flycatcherFicedula parvaLCPM104MuscicapidaeBluethroatLuscinia svecicaLCWV105Indian robinSaxicoloides fulicatusLCR106Black redstartPhoenicurus ochrurosLCWV107Common stonechatSaxicola torquataLCR108Pied bushchatSaxicola caprataLCR109Variable wheatearOenanthe picataLCR110Desert wheatearOenanthe desertiLCWV111SturnidaeRosy starlingPastor roseusLCDPM112Common starlingSturnus vulgarisLCWV113Common mynaAcridotheres tristisLCR114Bank mynaAcridotheres ginginianusLCR115HirundinidaePlain MartinRiparia paludicolaLCR116Barn swallowHirundo rusticaLCW117Wire-tailed swallowHirundo smithiiLCSM118PycnonotidaeWhite-eared bulbulPycnonotus leucotisLCR119Red-vented bulbulPycnonotus caferLCR120PellorneidaeRufous-vented priniaPrinia burnesiiNTR121CisticolidaeRufous-fronted priniaPrinia buchananiLCR122Yellow-bellied priniaPrinia flaviventrisLCR123Plain priniaPrinia inornataLCR124Graceful priniaPrinia gracilisLCR125Common tailorbirdOrthotomus sutoriusLCR126ZosteropidaeIndian white-eyeZosterops palpebrosusLCR127SylviidaeLesser whitethroatSylvia currucaLCWV128Yellow-eyed babblerChrysomma sinenseLCR129PhylloscopidaeCommon chiffchaffPhylloscopus collybitaLCWV130LeiothrichidaeCommon babblerTurdoides caudataLCR131Striated babblerTurdoides earleiLCR132Jungle babblerTurdoides striataLCR133AlaudidaeCrested larkGalerida cristataLCR134Oriental skylarkAlauda gulgulaLCR135NectariniidaePurple sunbirdCinnyris asiaticusLCR136PasseridaeHouse sparrowPasser domesticusLCR137Spanish sparrowPasser hispaniolensisLCDPM138Sind sparrowPasser pyrrhonotusLCR139MotacillidaeWhite wagtailMotacilla albaLCWV140White-browed wagtailMotacilla maderaspatensisLCR141Citrine wagtailMotacilla citreolaLCWV142Yellow wagtailMotacilla flavaLCDPM143Paddyfield pipitAnthus rufulusLCR144Tawny pipitAnthus campestrisLCR145Tree pipitAnthus trivialisLCSBV146PloceidaeBlack-breasted weaverPloceus benghalensisLCR147Streaked weaverPloceus manyarLCR148Baya weaverPloceus philippinusLCR149EstrildidaeScaly-breasted muniaLonchura punctulataLCR150EmberizidaeGrey-necked buntingEmberiza buchananiLCWLC: least concerned; VU: vulnerable; NT: near threatened; E: endangered; R: resident; WV: winter visitor; WM: winter migrant; W: wintering; PM: passage migrant; DPM: double passage migrant; SBV: summer breeding visitor.The current study showed that little cormorant was found more dominant with relative abundance of 10.59%, followed by common starling (5.47%), house crow (4.14%), sind sparrow (3.87%), cattle egret (3.73%), common myna (3.49%), black kite (3.21%), and common pochard (3.03%). The dominance of these species could be brought by high encounter rates and the presence suitable habitats on Taunsa Barrage wetland. The availability of food and favorable habitat makes some birds with a more abundance in the area [49]. Some other species such as barred buttonquail, pied cuckoo, peregrine falcon, steppe eagle, and short-toed snake eagle were observed only once throughout the study period.Out of the total bird species, 4 species (2 VU and 2 E) were recorded during the study period. The spotting of globally threatened species highlights the importance of Taunsa Barrage as an important wetland for bird species. Black-bellied tern (E), steppe eagle (E), common pochard (VU), and greater spotted eagle (VU) were regularly found at study site 3 (TP.3). This study site had a lowest human disturbance, wintering area, and feeding grounds for birds especially waterfowls and migratory birds. These results are consistent with the work of Mishra et al. [11] who stated that bird diversity and abundance depend on wetland characteristics such as food availability, quality of water, wintering, and breeding grounds. These findings also supported by the previous study conducted at Taunsa Barrage Wildlife Sanctuary [24, 26]. We also documented other threatened species (NT) such as ferruginous duck, Eurasian curlew, northern lapwing, river tern, oriental darter, and rufous-vented prinia.The present study duration restricted to seven months’ majority in winter season. Most of the bird species coming into the winter season in the study area were observed such as black-throated thrush, common kestrel, Eurasian curlew, Eurasian hobby, Eurasian sparrowhawk, Eurasian wryneck, grey-necked bunting, northern lapwing, and steppe eagle. Some winter visitor species such as waterfowls, cranes, and waders stay at the study site over winter until late February. These winter migratory bird species exhibit a distinct species-specific pattern for arrival at and departure from the Taunsa Barrage wetland. The arrival of these bird species further adds to the increase in diversity and abundance of total avifaunal population in the study area. These winter birds that migrate from the North (mainly from Russia) have been frequently visiting Taunsa Barrage [25].Out of total species, 19 species of raptors (Birds of Prey) were recorded during the present study. Bibi [26] recorded 16 raptor species from TBWS during 2009-2011. The following 8 raptor species such as common kestrel, Eurasian hobby, Eurasian sparrowhawk, Indian scops owl, peregrine falcon, white-eyed buzzard, short-toed snake eagle, and steppe eagle were not recorded by Bibi [26]. The Indian scops owl and Eurasian hobby raptor species are new records from the Taunsa Barrage. During this study, 11 species of raptors were found to be winter visitors and 8 species were residents. The maximum number of individuals of raptor species was 966 which were of Black Kite, and the minimum number of individuals observed was 1 of Eurasian sparrowhawk, peregrine falcon, steppe eagle, and short-toed snake eagle.The annual bird population trends at TBWS were observed from 2008 to 2014 by Bibi et al. [23]. The latter authors observed a decreasing trend of 14 bird species and an increasing trend of 157 bird species from 2008 to 2014. Among the 14 species, the white-backed vulture, greater painted snipe, Pallas’s fish eagle, and imperial eagle species were not documented during the current study. The previous study confirmed the rarity of white-backed vulture and imperial eagle (100% decline) in the study area. No records of their occurrence in the study area were found during the present study. Even interviews with local peoples revealed that these species had not visited the Ramsar site during the current study period, mainly due to habitat loss, chemical poisoning, trapping of birds, and hunting. Bibi et al. [23] found that alteration in the habitat, illegal hunting, and grazing had decreased the avifauna species population of the area. Their study confirmed that avian heritage of this wetland is under threat due to increased anthropogenic activities resulting in habitat destruction and fragmentation/deforestation.Khaliqet al. [25] reported that the population of 4 species such as oriental darter, Eurasian wigeon, pheasant-tailed jacana, and black-tailed godwit at TBWS were decreasing trend. During the present study, one species (black-tailed godwit) was not recorded and the other three were recorded in few numbers. Black-tailed godwit species were also not recorded in the Taunsa Barrage by Ali et al. [22]. Results of the current study confirmed the rarity of these birds in the study area. Ghalib et al. [50] carried out a study on birds of KPAC, Sindh, during September 2012 to March 2013. Their study period (September to March) is similar to the present study. Ghalib et al. [50] recorded 207 avian species belonging to 15 orders and 38 families.Bibi and Ali [24] reported Shannon-Wiener and Simpson’s diversity values of 3.39 and 0. 93, respectively, in the same study area (TBWS). In our study, higher diversity index values at Transect Points 2 and 3 revealed that species composition and diversity of birds at these sites were more diverse and distributed. At these sites, the level of human disturbance was low. Avian diversity and richness in TP 2 and 3 were high, because at these sites the human disturbances were very low and a safe place for bird feeding and other activities. Diversity and species richness in TP 1 and 4 were low due to anthropogenic activities and hunting at these sites. At these sites, the level of human disturbance was high. However, Transect Points 1 and 4 had the lowest species richness and diversity. The results of ANOVA revealed that there were no statistically significant differences across the months because this study restricted to winter season. Mean values of the total number of individuals were recorded during September 2019 to March 2020 (df=6, F=1.34, p=0.233) indicating no significant change month wise in bird diversity. The mean values of total individuals documented at four transects (F=4.800, df = 3, p=0.002) were significantly different (p<0.05). The ANOVA results showed that there were significant variances in bird diversity across four different transects during the study period.


## 5. Conclusion

Our study concluded that Taunsa Barrage wetland is very important to avian communities. Bird species richness, diversity, and abundance were compared in four different transects of the Taunsa Barrage Ramsar site. A total of 150 bird species were recorded belonging to 19 orders and 53 families. Shannon winner diversity index and evenness values revealed a more diverse and evenly distributed bird assemblage during September and October month. Similarly, higher diversity index values at Transect Points 2 and 3 revealed that species composition and diversity of birds at these sites were more diverse and distributed. More bird diversity was found in the low and medium human disturbance study sites. However, assessment of bird population status and trends from the Taunsa Barrage Ramsar site deserves the utmost significance for bird conservation.



---

*Source: 4736195-2022-05-19.xml*