Population Structure and Habitat Utilization of Migratory Birds at Bakhira Bird Sanctuary, Uttar Pradesh, India

Himanshu Mishra, Vikas Kumar and Ashish Kumar*

Animal Diversity and Ecology Laboratory, Department of Zoology, University of Lucknow, Lucknow-226007 U.P., India

ABSTRACT

An attempt has been made for the very first time to study the population structure and habitat utilization of migratory birds at Bakhira bird sanctuary, district Sant Kabir Nagar, Uttar Pradesh, India from October 2017 to March 2018. Thirty two species of birds were observed during the field investigation. The line transect method was employed for population estimates. During the field survey, we recorded a significantly higher number of migratory birds at the end of early winter (December) and at the commencement of middle winter (January). Red crested pochard (Netta rufina), Common coot (Fulica atra) and Gadwall (Mareca strepera) were the most populated species in the present study. The number of birds was not significantly different among winter months except between October/December and October/January wherein, we found significant variation in the number of birds at the Bakhira tal. Of the five main habitat types viz. lowland vegetation, upland vegetation, emergent vegetation, open water and agricultural fields, the most utilized were lowland vegetation and the emergent vegetation in the early and middle wintering stage. While in late winter, the emergent vegetation was the most utilized habitat. The findings of the present study provide the baseline information about the population of migratory birds and the rate of habitat utilization at the Bakhira bird sanctuary.

Article Information

Received 20 November 2018

Revised 11 May 2019

Accepted 20 June 2019

Available online 30 October 2019

Authors’ Contribution

AK planned this research. HM and VK performed field surveys, bird identification and population census. HM analysed the data and wrote the article.

Key words

Bakhira bird sanctuary, Habitat utilization, Migratory birds, Population structure, Wetland

DOI: https://dx.doi.org/10.17582/journal.pjz/2020.52.1.247.254

* Corresponding author: [email protected]

0030-9923/2020/0001-0247 $ 9.00/0

Copyright 2020 Zoological Society of Pakistan

INETRODUCTION

Wetlands can be broadly defined as intermediary land between terrestrial and aquatic ecosystems, where the water table is typically at or near the surface or the land is enclosed by shallow water (Mitsch and Gosselink, 1986). Wetlands cover an area of 58.2 million hectares in India (Prasad et al., 2002). Of the 9702 bird species reported worldwide (Sibley and Monroe, 1990), 1313 species have been recorded from the Indian subcontinent (Grimmett et al., 2011). India has more than 1200 species of birds which is over 13% of the world’s avifauna (Kumar et al., 2005). According to Kumar et al. (2005), 310 species are known to depend particularly on wetlands, of which 107 species are winter migrants. Among the, migratory birds waterfowl are one of the main components of global biodiversity (Li and Mundkur, 2004). Many important migratory bird species visit India from October to March (Rahmani et al., 1997). Wetlands support the highest number of water birds during the winter. Wetlands are considered important conservation sites due to the extensive food chain and rich biodiversity they hold (Getzner, 2002).

Migration is a common phenomenon in eukaryotes. It is the consequence of complex interaction between intrinsic (genetic, physiological and behavioural) and extrinsic factors (weather, habitat condition, food availability, predation, topography (Akesson and Hedenstrom, 2007). Migration in birds is an inclination that has fascinated researchers and naturalists all over the world. The identification of effects and timing of limiting factors for migratory birds is rather difficult, because of the momentary interconnected nature of migration conditions throughout the annual cycle (Sillett and Holmes, 2002).

Habitat use is defined as the way in which an individual or species uses the habitat to fulfill the life history needs (Jones, 2001). Three factors are important in habitat selection by birds viz. food availability, protection from predators and constraints imposed by morphological characteristics (Hilden, 1965). In recent years, due to the over-exploitation of resources, wetland deprivation has become a serious issue that has resulted in habitat shrinkage for migratory water birds. According to a group of researchers food resource utilization is regarded as the interspecific competition among wintering waterbirds, that may be intensified by food shortages (Xiang and Wang, 2005; Wang et al., 2011). Food, space and other resources are extremely limited in degraded wetlands, particularly during cold and severe winters. The competitive intensity of waterfowl generally peaks at this time (Oksanen, 1987).

The review of literature suggests that so far, no research has been carried out on population structure and habitat utilization of migratory birds at Bakhira bird sanctuary, district Sant Kabir Nagar, Uttar Pradesh, India. Therefore, the present study was undertaken to collate comprehensive information about the population structure and habitat utilization of migratory birds in the study area. In India some researchers have reported pattern of habitat utilization in wetland birds particularly in Kerala and Chhattisgarh (Sharma et al., 2014; Roshnath and Shruthi, 2015).

 

MATERIALS AND METHODS

Study area

Bakhira bird sanctuary also known as Bakhira Tal (N 26°54’ E 83°06’) located to the west of the Rapti river bank, is a shallow-water, river-connecting wetland, declared a bird sanctuary in 1990 by the Forest and Wild life Department, Uttar Pradesh, India vide order number 822/14-3-60/1989, dated 14/5/1990 (Fig. 1a). The google image of Bakhira bird sanctuary has been placed in Figure 1b while Figure 1c shows the representative image. It is part of the natural floodplain in Uttar Pradesh, expanding over an area of 29 km2. The landscape and terrain of the wetland are approximately flat having an average elevation of 100 meters above mean sea level representing a typical terai landscape. The vegetation in the wetland mainly consists of Typha angustifolia, Phragmites karka, Eichhornia crassipes, Hydrilla verticillata, Vallisneria spiralis and Lemna minor (Mishra and Narain, 2010). It facilitates the wintering and staging ground for many migratory waterfowl and breeding ground for resident (and summer migrating) birds (Mishra et al., 2016). We identified five habitat types viz upland vegetation, lowland vegetation, emergent vegetation, open water and agricultural fields. An exhaustive study was carried out from October 2017 to March 2018 to determine the population structure and habitat utilization of migratory birds.

The wintering season was divided into three stages according to hydrological variations in the wetland as follows: (1) The early phase of wintering season from October to late December. During this period, the wetland is still at a high water but starts to retreat; (2) The middle stage from early January to late February in the year, when the water level drops and large areas of the wetland shore become exposed; (C) The late phase from late February to the end of March, in which the wetland shore becomes drier and the water level begins to decline.

Population survey

Birds were counted using 15-minute line transect count (3 observations/hour×3 hour per day ×4 days/ month

 

with the settlement period of 5 minutes between 2 observation sessions) in which we traversed a line and reordered birds as the target objects method (Burnham et al., 1980). During each visit birds were counted three times from 6.0-7.0 am, 11.0 am-12.0 hours and 4.0-5.0 pm respectively. A total of 216 (36/month×6) observations were recorded to estimate mean number of migratory birds.

Migratory bird survey was conducted randomly at 5-6 day intervals in a month. A total of 36 surveys (6 surveys per month) were undertaken during the study period. The counting of migratory birds was done by 5-6 main observers to avoid double counting. The bird identification was carried out with the aid of key reference books Ali (2002); Grewal et al. (2002) and Grimmett et al. (2007).

 

Habitat utilization

The habitat utilization rates (U) of all habitat types by these migratory birds was calculated as per Zhao et al. (2013).

Where Ui is the utilization rate of the ith habitat type by water birds; Ni the number of water birds in the ith habitat type and N the total number of water birds in all habitat types.

Statistical analysis

Population structure of migratory birds was analyzed by Analysis of Variance (One way ANOVA) followed by Tukey´s post hoc test. All the statistical analyses were carried out using PAST (version 3.12) and Graph Pad Prism (version 5.01).

 

RESULTS

Population structure

Population status of migratory birds was significantly (p=0.030) high at the end of early winter (December) and commencement of middle winter (January) (Table Ι). Red crested pochard (Netta rufina) (46.5±9.79), Common coot (Fulica atra) (45.1±8.42) and Gadwall (Mareca strepera) (35.6±9.13) outnumbered other species (Table Ι). Tukey´s post hoc test showed that there was no significant difference (p>0.05) in the number of birds among winter months (Table ΙΙ) although significant variation (p<0.05) was apparent in the number of birds between October/December and October/January (Table ΙΙ).

Habitat utilization

In order to estimate habitat utilization rate, there were eight (8) observations (4 observations/month/ wintering stages) each were recorded for each wintering stage. The most utilized habitat type was lowland vegetation (p=0.0267) at the early wintering stage, with a utilization rate 0.427±0.021 followed by 0.254±0.027 for the emergent vegetation. The utilization rates of open water areas, upland vegetation and agricultural fields were relatively low, i.e., 0.152±0.028, 0.134±0.169 and 0.058±0.022 respectively. The most frequently utilized habitats at the middle wintering stage were lowland vegetation (p=0.0124) and emergent vegetation (p=0.0124) with a utilization rate of 0.351±0.028 and 0.346±0.023 followed by 0.136±0.025, 0.131±0.019 and 0.062±0.020 for agricultural fields, upland vegetation and open water respectively. The utilization rate at the late wintering stage of emergent vegetation was 0.58±0.220, which was evidently higher (p=0.032) than that of other habitats. The utilization rate was 0.337±0.031, 0.156±0.022, 0.059±0.021 and 0.052±0.023 for shallow-water areas, open water areas, agricultural fields and upland vegetation respectively.

 

DISCUSSION

Population structure

The findings of the study revealed a diverse migratory bird population in the study area. In the present study, 32 species (8 orders and 11 families) of migratory birds were recorded which is in agreement with the finding of Harisha and Hosetti (2018) at Komaranahalli Lake, Davanagere District, Karnataka, India (November 2012 to October 2013). The peak population of migratory birds was recorded during the months of December and January. Almost all of them left the wetland by the end of March.

 

Table Ι. Population structure of migratory birds during winter season in 2017-2018.

Order	Family	Species	Scientific name	Oct	Nov	Dec	Jan	Feb	Mar	Mean ±SD
				Mean±SD
Acciptri-formes	Accipi-tridae	Oriental honey buzzard	Pernis ptilorh-yncus	25 (0.81)	26 (1.29)	24 (0.84)	24 (0.75)	22 (1.71)	19 (2.8)	23.3± 2.50
		Black baza	Aviceda leuphotes	2 (0.54)	3 (0.83)	3 (0.74)	2 (0.68)	1 (0.32)	0 (0)	1.8± 1.16
		Egyptian vulture	Neophron percno-pterus	0 (0)	2 (0.58)	3 (0.79)	3 (0.35)	2 (0.21)	2 (0.17)	2± 1.09
		Tawny eagle	Aquila rapax	5 (0.75)	7 (1.14)	7 (1.12)	9 (1.21)	8 (1.16)	4 (0.85)	6.6± 1.86
		Hen harrier	Circus cyaneus	8 (1.25)	12 (2.63)	14 (1.67)	14 (1.25)	12 (0.59)	9 (0.78)	11.5± 2.50
		Black winged kite	Elanus caeruleus	15 (1.50)	18 (2.24)	20 (2.06)	14 (1.41)	13 (1.90)	10 (1.65)	15 ± 3.57
		Greater spotted eagle	Clanga clanga	0 (0)	1 (0.52)	1 (0.63)	2 (0.32)	2 (0.47)	1 (0.41)	1.16 ±0.75
		Lesser spotted eagle	Clanga pomarina	2 (0.73)	3 (0.89)	2 (0.53)	2 (0.58)	1 (0.35)	1 (0.42)	1.8 ±0.75
Anseri-formes	Anati-dae	Common teal	Anas crecca	20 (3.01)	30 (2.60)	34 (2.15)	36 (2.65)	36 (2.17)	30 (1.53)	30.66667
		Spot billed duck	Anas poecilo-rhyncha	14 (1.33)	18 (1.28)	22 (2.14)	24 (2.11)	23 (2.34)	21 (2.16)	20.3± 3.72
		Mallard	Anas platyrhnchos	15 (0.85)	25 (2.16)	29 (1.95)	30 (1.39)	29 (2.24)	22 (2.11)	25± 5.76
		Gadwall	Mareca strepera	29 (2.36)	32 (2.17)	44 (1.78)	48 (3.26)	37 (1.23)	24 (1.86)	35.6 ±9.13
		Eurasian wigeon	Mareca penelope	4 (1.49)	8 (1.59)	15 (1.79)	11 (2.86)	8 (1.98)	5 (1.98)	8.5 ±4.03
		Garganey	Spatula querquedula	16 (1.85)	34 (2.68)	40 (2.73)	42 (2.15)	35 (3.96)	21 (2.33)	31.3 ±10.50
		Tufted pochard	Aythya fuligula	12 (1.22)	16 (2.59)	22 (1.19)	17 (3.36)	13 (1.65)	8 (0.75)	14.6 ±4.80
		Ruddy shelduck	Tadorna ferruginae	0 (0)	2 (0.52)	6 (0.21)	7 (0.36)	6 (0.55)	4 (0.17)	4.1± 2.71
		Northern shoveler	Spatula clypeata	0 (0)	14 (2.31)	15 (0.89)	16 (1.38)	15 (1.88)	12 (1.22)	12±
		Cotton pygmy goose	Nettapus coromand-elianus	12 (1.85)	17 (2.31)	19 (2.15)	24 (2.11)	22 (2.55)	18 (2.67)	18.6± 4.18
		Graylag goose	Anser anser	25 (3.19)	38 (3.98)	44 (2.66)	42 (3.26)	41 (3.45)	29 (2.14)	36.5± 7.71
		Northern pintail	Anas acuta	0 (0)	12 (1.55)	14 (1.48)	15 (1.11)	12 (0.96)	11 (1.38)	10.6± 5.42
		Bar headed goose	Anser indicus	14 (1.62)	18 (1.65)	28 (2.46)	30 (2.28)	25 (2.46)	21 (1.97)	22.6± 6.12
		Red crested pochard	Netta rufina	40 (2.86)	45 (2.15)	56 (2.76)	58 (3.10)	48 (3.26)	32 (2.67)	46.5± 9.79
Cuculi-formes	Cucu-lidae	Jacobin cuckoo	Clamator jacobinus	5 (0.56)	6 (0.31)	6 (0.12)	8 (0.98)	5 (0.34)	4 (0.19)	5.7± 1.36
Columbi-formes	Colum-bidae	Oriental turtle dove	Streptopelia orientalis	4 (0.25)	8 (0.68)	8 (0.45)	12 (0.15)	11 (1.21)	8 (0.49)	8.5± 2.81
	Scolop-acidae	Wood snipe	Gallinago namoricola	0 (0)	0 (0)	5 (0.46)	4 (0.13)	4 (0.16)	2 (0.01)	2.5± 2.16
		Common redshank	Tringa totanus	26 (2.78)	29 (2.96)	32 (2.44)	34 (2.59)	25 (2.03)	21 (1.97)	27.8± 10.08
		Little stint	Calidris minuta	24 (2.02)	28 (2.36)	30 (3.14)	28 (3.26)	23 (2.19)	19 (2.05)	25.3±
	Larid-ae	Common tern	Sterna hirundo	16 (2.14)	19 (2.32)	28 (3.25)	27 (2.99)	24 (2.13)	22 (2.56)	22.6± 4.63
Ciconii-formes	Cicon-iidae	European white stork	Ciconia ciconia	18 (1.53)	19 (1.29)	25 (2.12)	24 (2.39)	22 (1.37)	21 (1.04)	21.5± 2.73
Gruifo-rmes	Rall-idae	Common coot	Fulica atra	39 (3.27)	41 (3.39)	54 (2.23)	58 (2.96)	50 (3.92)	35 (2.91)	45.1± 8.42
Passeri-formes	Dicru-ridae	Fork tailed drongo	Dicrurus adsimilis	8 (0.36)	8 (0.25)	10 (1.20)	12 (1.14)	11 (0.96)	7 (0.38)	9.3± 1.96
Pelecan-iformes	Arde-idae	Grey heron	Ardea cinerea	12 (0.96)	14 (1.23)	21 (1.26)	20 (1.49)	18 (1.53)	12 (1.11)	16.1± 4.02

 

Table ΙΙ. Tukey´s multiple comparisons test among all months during winter season 2017-2018. A-October, B-November, C- December, D-January, E- February, F-March.

Tukey's Multiple Comparison Test	Mean difference	q	Significant? P < 0.05?	Summary	95% CI of diff
Column A vs Column B	-4.949	2.51	No	ns	-13.02 to 3.123
Column A vs Column C	-8.949	4.538	Yes	*	-17.02 to -0.8773
Column A vs Column D	-9.128	4.63	Yes	*	-17.20 to -1.057
Column A vs Column E	-6	3.043	No	ns	-14.07 to 2.071
Column A vs Column F	-1.333	0.6762	No	ns	-9.405 to 6.738
Column B vs Column C	-4	2.029	No	ns	-12.07 to 4.071
Column B vs Column D	-4.179	2.12	No	ns	-12.25 to 3.892
Column B vs Column E	-1.051	0.5332	No	ns	-9.123 to 7.020
Column B vs Column F	3.615	1.834	No	ns	-4.456 to 11.69
Column C vs Column D	-0.1795	0.09103	No	ns	-8.251 to 7.892
Column C vs Column E	2.949	1.495	No	ns	-5.123 to 11.02
Column C vs Column F	7.615	3.862	No	ns	-0.4560 to 15.69
Column D vs Column E	3.128	1.587	No	ns	-4.943 to 11.20
Column D vs Column F	7.795	3.953	No	ns	-0.2765 to 15.87
Column E vs Column F	4.667	2.367	No	ns	-3.405 to 12.74

 

The basic need of migratory water birds at their wintering sites includes adequate food and shelter (Lakshmi, 2006). The study indicated a stable or increasing migratory bird trend at Bakhira bird sanctuary which was found to be in agreement with stable or increasing status of their major food-bases. Waterbird abundances is intricate to interpret because different factors often act simultaneously, confounding the effects of individual ones (Chalfoun and Martin, 2007). The correlation between waterbirds and wetland variables may be simple reflection of some decisive habitat features, frequently correlated with food-bases, which are not readily measured (Terborgh, 1985). Relative abundance of birds depends upon wetland features such as size, water level, quality of water, availability and distribution of food resources and the presence of appropriate roosting and nursery sites (Terborgh, 1985).

Skagen et al. (1999) are of the view that interior wetland complexes are endowed with critical refueling resources along the direct routes between summering and wintering grounds. Migratory birds face tremendous ecological and physiological challenges during long-distance migrations.

In addition to the vigorous expenditure flight, birds must find periodic stopovers to rest and refuel and to cope with unfavorable weather, uncertainties of resource abundance and accessibility, intra and inter-specific competition, and predation pressures, all within the context of unfamiliar environments (Moore et al., 2005). These challenges, in concert with wide-scale anthropogenic changes in habitats and landscapes along historical migratory pathways, espouse that intercontinental migration poses formidable hardships to many birds.

Habitat utilization

A variety of foraging habitat types and feeding techniques are used by migratory birds during the wintering season (Mishra et al., 2019). The most utilized habitat types were lowland vegetation and the emergent vegetation in the early and middle winter stages. Such condition of the particular sites of water bodies supporting greater densities and diversity of macro-benthic invertebrates has been well acknowledged by Kaminski and Prince (1981) who suggested that this usually occurred when the ratio of emergent vegetation and open water was almost equal (50:50). Moreover, macro-benthic invertebrates which correspond to the major diet of waterfowl (Chick and McIvor, 1994) were more intimately associated with aquatic vegetation than the barren substrate (Swanson et al., 1974; Joyner, 1980) as crumbling of the vegetation provided supplementary nutrients and surface for the proliferation and habitation of macro-invertebrates (Murkin et al., 1982).

Distinguished researchers such as Bellrose (1980) and Jones and Drobney (1986) also reported that waterbirds foraged profoundly on benthic macro-invertebrates. This confirms the present observation. The utilization rate of open water areas, upland vegetation and agricultural fields was quite low. The utilization rate of emergent vegetation was evidently higher than that of other habitats at the late wintering stage. Due to the decline in water level in late winter, low land vegetation was less utilized than emerging one. Habitat selection of wintering birds is influenced by prey availability and accessibility (Nagarajan and Thiyagesan, 1996). Availability of microhabitats and various food resources is the determining factors that controlled seasonal changes of bird species composition. The distribution of food is one of the most significant factors influencing the selection of feeding sites (Grant and Grant, 1987).

Water birds have to select appropriate habitats while facing constantly changing habitats during the winter (Warnock and Takekawa, 1995; Beerens et al., 2011). In many cases the decline in population involves groups of species that share the same habitat and have analogous ecological requirements, representing underlying causes for these population changes rather than a unique explanation for each species. Food preference of waterbirds can differ significantly among species, even among those within the same group (Zhu and Zou, 2001).

Waterbirds use different foods, including seeds (dabbling ducks, geese, cranes), leaves (geese), tubers and rhizomes (geese, swans), invertebrates (shorebirds, waterfowl), and some vertebrates for example fish and amphibians (wading birds). The amount, composition, and spatio-temporal dynamics of these foods primarily affect the use of foraging habitats by waterbirds and considered to be imperative indicators of habitat quality (Taft and Haig, 2005; Hartke et al., 2009). Wetlands could be important foraging habitats for waterbirds, particularly during wintering periods (Masero et al., 2000).

 

CONCLUSIONS

In conclusion, 32-species of migratory waders were recorded at Bakhira bird sanctuary. We concluded that all habitat types were efficiently utilized by migratory waders in all the wintering stages. Low vegetation was most frequently utilized habitat type in early winter stage. Low vegetation and emergent vegetation were evidently utilized habitat types in middle winter stage. Finally, emergent vegetation was suggested to utilize more prominently in late winter stage. The outcome of our study recommended that, Bakhira bird sanctuary may provides an efficient foraging and nesting ground for migratory birds as well as resident birds. We suggested some conservation measures for migratory waders as well as resident birds. The land use for human habitations should be discouraged to avoid agricultural drain off posing pollution threat. Control of aquatic microphytes is necessary in order to maintain optimal habitats. The weeds especially the emergent and floating types obstruct the waterways which should be thinned or removed by mechanical or manual measures. The wetland habitat being a famed and crowded bird sanctuary more effective steps from control of poaching should be recommended. For habitat preservation, the bird sanctuary should be fenced to afford a disturbance-free environment for birds and afford complete protection from illegal activities.

 

ACKNOWLEDGEMENTS

The authors would like to articulate their gratefulness to the Head, Department of Zoology, University of Lucknow, for providing facilities and administrative support. Himanshu Mishra is thankful to the University Grants Commission (UGC), New Delhi for Senior Research Fellowship [Ref. No. 21/12/2014 (ii) EU-V]. The authors are thankful to Ms. Farah bano, for her assistance in statistical analysis of the data. The authors are also grateful to the staff, Forest Department, Sohagibarwa, District Sant Kabir Nagar, Uttar Pradesh for their valuable support during field visits.

 

Statement of conflict of interest

The author declares that they have no conflict of interests.

 

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