House Sparrow Passer Domesticus_manjeri Munipality_kerala

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    Technical Report Submitted toWildlife Research and Conservation Trust

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    Technical Report Submitted toWildlife Research and Conservation Trust

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    Citation:

    Balakrishnan, P., Jijeesh, N., Kurikkal M. S., Maya T., Lijitha M. P., Bhaskar R. R. and N.Vipeesh. 2011. Distribution, abundance and nest site characteristics of the House SparrowPasser domesticus in Manjeri Municipality, Kerala. Technical Report submitted to WildlifeResearch and Conservation Trust. NSS College, Manjeri.

    Photographs:

    Jijeesh, N., Kurikkal, M.S. and P. Balakrishnan

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    Acknowledgement

    We are grateful to the Wildlife Research and Conservation Trust, Nilambur for funding this

    project. Special thanks to Dr. K.S. Anoop Das and T.N. Bindu for providing literature and

    support. We also thank the Principal, other staff members, our classmates and members of

    Hornbill Nature Club for their critical thoughts, and the shop keepers and residents of Manjeri

    for logistic support during this study.

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    1

    Contents

    Contents ......................................................................................................................................1

    Summary.....................................................................................................................................2

    1. INTRODUCTION...............................................................................................................3

    1.1. House sparrow: the study species ..................................................................................31.2.

    Global decline of House Sparrows ................................................................................4

    1.3. Goal and objectives .......................................................................................................5

    2. MATERIALS AND METHODS........................................................................................5

    2.1. Study area .....................................................................................................................5

    2.2.

    Field methods and data analysis ....................................................................................9

    2.2.1.

    House Sparrow surveys ..........................................................................................9

    2.2.2. Habitat and nest site characteristics ........................................................................9

    3. RESULTS.......................................................................................................................... 11

    3.1. Distribution and abundance of House Sparrows at Manjeri .......................................... 113.2.

    Habitat factors and distribution of House Sparrows ..................................................... 13

    3.3. Nest site characteristics of the House Sparrow population at Manjeri .......................... 14

    4. DISCUSSION AND CONCLUSION.................................................................................. 18

    5. REFERENCES.................................................................................................................. 19

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    Summary

    The status, habitat selection and the nest site characteristics of the House Sparrow Passer

    domesticus in the Manjeri Municipality were studied during December 2010 February 2011.

    The birds were counted by a line transect method (40 transects of 50 m length) along the main

    roads and by a total count method in the daily market. The core area of Manjeri town (2 km2)

    supports a reasonably large population of House Sparrows (>530 individuals). We recorded a

    maximum of 349 and 181 individuals from the road transects and the market, respectively.

    House Sparrow abundance and the number of nests in the road-transects were positively

    correlated to the numbers of buildings with cement-concrete roofs, rolling shutter doors, hotels

    and rice/cereal godowns. The number of nests was also positively associated with the number of

    grocery shops in the transects. The presence of vegetation in the transects had a negativecorrelation with the abundance of sparrows and the number of nests present. A total of 109 nests

    were recorded during the study and of these 84 nests were studied in detail to reveal the nest site

    characteristics of House Sparrows. All the nests were placed in human-made structures in the

    buildings or artificial boxes and baskets established by the shop keepers. Majority of the nests

    (89.3%, n= 75) were placed above the roller shutter boxes. The nests were placed at an average

    of 3.831.29 m above ground ranging from 2.5 6.3 m. In general the nests were placed in the

    close vicinity of grocery shops, rice godowns and hotels. As the House Sparrow populations in

    major cities are already disappeared, there is an urgent need to conserve the species in small

    towns like Manjeri, where it is still common for the long-term survival of the species.

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    1. INTRODUCTION

    In recent decades anthropogenic impacts have resulted in devastating biodiversity loss

    throughout the world. Urbanization and pollution are the most damaging and rapid form of

    anthropogenic pressure. Many rare species are known to be affected by urbanization andpollution (Ricketts et al., 2005; Mcdonald et al., 2008). Several widely distributed and common

    species like House Sparrow Passer domesticus(Linnaeus, 1758) are also facing massive decline

    across several countries due to anthropogenic pressures. It is important to understand the status

    and habitat relationships of a species in decline in order to allow the suggestion of effective

    conservation measures. The present study is an attempt to document the status, distribution and

    the nest site characteristics of House Sparrow in Manjeri Municipality, Kerala, South India.

    1.1.

    House sparrow: the study species

    The House Sparrowbelongs to the family Passeridae, occurs naturally in most of Europe, the

    Mediterranean region, and much of Asia. It has also been intentionally or accidentally introduced

    to many parts of the world, making it the most widely distributed bird species (Summers-Smith,

    1988). In the Indian subcontinent they are commonly found in India including introduced

    populations in Andaman Islands; Pakistan, Bangladesh, Sri Lanka and Maldives (Ali and Ripley,

    1987).

    The sexes are dimorphic with the male being boldly patterned. In male the crown is grey,

    lores and round eye black. The mantle and scapulars are boldly streaked black, chestnut and buff

    and the tail is dark brown. The female is grayish brown streaked with fulvous and dark brown on

    back. A pale supercilium and the under parts plain brownish white. The House Sparrows seen in

    pairs when breeding, otherwise in noisy flocks. They are unfailing commensal of man, primarily

    associated with cities and suburbs, villages, often even isolated homesteads, and human

    habitations of every description. The House Sparrow is primarily a seedeater, but also feeds on

    fruit and flower buds, tender shoots, kitchen scraps and insects. Nestlings are fed on soft bodiedinsects and caterpillars, etc. The breeding season is chiefly March to June in north, continuing till

    September or October in central India, but they breed throughout the year in south India (Ali and

    Ripley, 1987).

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    1.2. Global decline of House Sparrows

    During recent decades, there has been a marked global decline of the House Sparrow populations

    especially in the United Kingdom and in several western European countries. In England the

    populations in rural areas have declined by 47% since the mid 1970s, whereas those in urban andsuburban areas have declined by about 60% (Crick et al., 2002; Summers-Smith, 2003; Robinson

    et al., 2005; Vincent, 2005). Such declines have led to almost complete extinction in some urban

    centres; for example, there was a 71% decline in London from 19942002 (Raven et al., 2003).

    In Europe, trends since 1980 show that populations have undergone a moderate decline, based on

    provisional data for 21 countries from the Pan-European Common Bird Monitoring Scheme

    (BirdLife International, 2011). Further to these declines the House Sparrow was added to the Red

    List of U.K. endangered species in 2002 (Summers-Smith, 2003) and in Germany, it is classified

    as near threatened (Bauer et al. 2002) due to the large scale local declines. However, BirdLife

    International (2011) listed House Sparrow as a Least Concern species as it has an extremely

    large range and population size.

    A number of hypotheses have been put forward to explain the population decline of the

    House Sparrows. These include lack of food, primarily aphids, which adults feed to nestlings,

    inter-specific competition for food, loss of nesting sites, particularly under the eaves and in the

    roofs of houses, cleaner streets providing reduced foraging opportunities, disease transmission

    (e.g. salmonella), increased predation, pollution from vehicles running on unleaded fuel,

    pollution (air quality), both in terms of immediate toxicity and indirect toxicity through the food

    supply and increased use of pesticides in parks and gardens (Crick et al., 2002; Summers-Smith,

    2003; Vincent, 2005; Peach and Vincent, 2006). Recent studies also support the notion that

    long-term exposure to higher levels of radiation negatively affects the abundance or behavior of

    House Sparrows (Balmori and Hallberg. 2007; Everaert and Bauwens, 2007).

    Although there is a growing concern over the decline of House Sparrows in India (Vijayan,

    2003; Daniels, 2008; Joshi, 2009; Dandapat et al, 2010)there has been limited research aimed atdetermining the population dynamics and geographical distribution and causes of declines (see,

    Balakrishnan, 2005; Goyal, 2005; Rajashekar and Venkatesha, 2008; Dhanya and Azeez, 2010;

    Ghosh et al., 2010). It is important that systematic surveys and comparisons of house sparrow

    populations to be conducted in order to assess differences in abundance and breeding

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    productivity within different areas of the same city and between different urban landscapes with

    different socio-economic, technological and cultural characteristics (see, Crick et al., 2002).

    1.3. Goal and objectives

    The goal of this was to gather information on the status of House Sparrow at a local scale and

    thereby contribute to its conservation. The specific objectives were to:

    assess the status, distribution and abundance of the House Sparrow population in Manjeri

    Municipality,

    identify the correlates of the distribution of the House Sparrow with the habitat features,

    and

    obtain information on the nest site characteristics of House Sparrows.

    2. MATERIALS AND METHODS

    2.1. Study area

    This study was conducted in Manjeri Municipality (1107 N & 7607E and 11.12N &

    76.12E) the commercial capital of Malappuram District in Kerala State in Southern India. The

    municipality of Manjeri comprises 53.06 km2, across three villages and 50 wards (Figure 1). The

    average elevation is 38 metres (124 feet). The climate is typical tropical with an average

    temperature around 31.5 C. The average maximum and minimum temperature and rainfall andnumber of rainy days per month are presented in Figures 2 and 3. The municipal area can be

    divided in two well differentiated areas: the core town area and surrounding agricultural and

    residential areas with very small towns. The main town area composed largely of several

    shopping centres and office buildings, most having two or more stories and few residential

    houses. The rural area of the municipality is composed of small hilly agricultural fields with

    coconut, rubber, arecunut and cashew as the main crops and bordering some riverine habitats.

    The Manjeri Municipality was formed on 1st April 1978. Manjeri is inhabited by more than

    83,704 people and population density is 1307 / km2(2001 census). During the last 10-20 years

    majority of the old buildings in the town are replaced with cement-concrete buildings. The area

    where the intensive study was carried out, had an approximate area of 3 km2and was located in

    the middle of the Municipality. The intensive sites include the permanent market (1ha) and the

    four main roads towards Malappuram, Kozhikode, Nilambur and Pandikkad (Figure 4; Plate 1).

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    Figure 1. Map of Manjeri Municipality showing the study location

    Figure 2.Average maximum and minimum temparature at Manjeri.

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    Figure 3.Average monthly rainfall and number of rainy days per month at Manjeri.

    Figure 4.Map Showing the intensive sampling locations

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    Plate 1. a). view of Manjeri Town; b). a close view of one of the road-transects

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    2.2. Field methods and data analysis

    2.2.1. House Sparrow surveys

    The preliminary surveys conducted in various regions of the Manjeri Municipality indicated that

    the House Sparrow population is restricted to the core area of the town. Two methods were

    employed to assess the abundance of sparrows. A total count method was used to survey the

    birds in the market (1ha) area. In the second method we counted sparrows along 40 line

    transects, 50-m long located in the four main roads of the town. All the four main roads had

    equal number of transects (10 each). The surveys were repeated three times during December

    2010, January and February 2011. All the surveys were conducted between sunrise and 2 h after

    sunrise and were not conducted during precipitation or windy conditions. The numbers of males

    and females sparrows were recorded separately during each survey. Apart from this, the total

    number of nests was also recorded separately for each transect.

    2.2.2. Habitat and nest site characteristics

    In each of the 40 road-transects, a number of structural features were measured in order to

    characterize the habitat characteristics. The habitat features measured include a number of

    structural characters of the buildings, presence of food sources and vegetation (see Table 1).

    Table 1.Descriptions of habitat features measured at each 50m line transects.

    Code Variable Description

    DRFT Dominant roof type Classified as concrete and tile roofs

    NCRF Concrete roof No. of buildings with concrete roofs

    NTRF Tile roof No. of buildings with tile roofs

    NSHTR Shutterhood (#) No. of shutters on either sides

    NHTL Hotels (#) No. of hotels

    NGCS Grocery shops (#) No. of grocery shops

    NGDNS Godowns (#) No. of godowns

    NWLS Wells (#) No. of wells

    NWPS Water pipes (#) No. of water pipes

    NTREES Trees (#) No. of trees

    NGRASS Grass (#) No. of grass patches

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    The nests were located by searching all the probable nest sites like shutter boxes,

    ventilators, shelter boards, trees, artificial boxes, etc., in all the transects and the market and also

    by observing the behaviours of birds (moving with nest materials, food, etc.). To characterize thenest site characteristics we measured habitat characteristics of 84 nests of House Sparrows. The

    variables measured include the nest site, height from ground, visibility of nest and several

    parameters related to the food supply. Detailed descriptions of the variables and the method of

    measurements are given in Table 2.

    The meanSD values are presented for habitat and nest site characteristics. A Spearman

    rank correlation matrix was also calculated to understand the importance of habitat variables on

    the abundance of sparrows and number of nests in the transects. The nest site characteristics of

    the nests placed in the market and transects were compared using MannWhitney U test.

    Table 2. Descriptions of habitat features measured at the nesting sites of House Sparrow atManjeri.

    Code Variable Description

    NSITE Nest site Classified as Shutter, ventilator,

    shelter boards or artificial boxes

    HTGD Height from ground (m) Nest height above ground

    VSNT Visibility of nest (%) % visibility of nest

    SHTR Shelter above nest (m) Shelter distance in front of the nest

    DNNT Distance from nearest nest (m) Distance to the nearest nest

    DHTL Distance from nearest hotel (m) Distance to the nearest hotel

    DGWN Distance from nearest godown (m) Distance to the nearest rice godown

    DGSH Distance from nearest grocery shop (m) Distance to the nearest grocery shop

    DGAD Distance from nearest garden (m) Distance to the nearest garden

    DVEG Distance from nearest vegetation (m) Distance to the nearest patch ofvegetation or tree

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    3. RESULTS

    3.1. Distribution and abundance of House Sparrows at Manjeri

    The core area of Manjeri town (2 km2) supports a reasonably large population of House

    Sparrows (>530 individuals). We recorded an average of 301.33 (52.63) and 172 (12.3) House

    Sparrows with a maximum of 349 and 181 individuals from the road transects and the market,

    respectively. We detected between 0 43 (mean SD: 4.291.79) male and between 0 26

    (mean SD: 3.241.47) female Sparrows on each transect over the three surveys. Raw counts of

    the male and female House Sparrows during the three different counts in the market and along

    the 50 m long transects in the four main roads are presented in Table 3 and Tables 4 to 7,

    respectively.

    Table 3.Number of House Sparrows recorded in the municipal market, Manjeri.

    Count 1 Count 2 Count 3 TotalnestsMale Female Total Male Female Total Male Female Total

    97 61 158 108 73 181 107 70 177 35

    Table 4.Number of House Sparrows recorded in the transects along Nilambur Road, Manjeri.

    Transect

    Name

    Count 1 Count 2 Count 3 Total

    nestsMale Female Total Male Female Total Male Female Total

    Nlbr 1 4 3 7 4 3 7 6 4 10 3

    Nlbr 2 0 0 0 0 0 0 0 0 0 0

    Nlbr 3 4 3 7 6 3 9 9 6 15 3

    Nlbr 4 0 0 0 0 0 0 0 0 0 0

    Nlbr 5 1 1 2 2 3 5 3 2 5 2

    Nlbr 6 0 0 0 0 0 0 1 0 1 0

    Nlbr 7 0 0 0 0 0 0 1 0 1 0

    Nlbr 8 2 1 3 0 0 0 2 2 4 1

    Nlbr 9 2 2 4 3 2 5 3 2 5 1

    Nlbr 10 0 0 0 0 0 0 1 0 1 0

    Total 13 10 23 15 11 26 26 16 42 10

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    Table 5.Number of House Sparrows recorded in the transects along Pandikkad Road, Manjeri.

    Transect

    Name

    Count 1 Count 2 Count 3 Total

    nestsMale Female Total Male Female Total Male Female Total

    Pkd 1 8 11 19 11 15 26 10 14 24 2

    Pkd 2 12 14 26 19 26 45 9 9 18 8

    Pkd 3 4 3 7 6 5 11 0 0 0 1

    Pkd 4 2 1 3 3 1 4 5 3 8 3

    Pkd 5 4 5 9 6 4 10 8 6 14 8

    Pkd 6 10 13 23 16 18 34 16 19 35 9

    Pkd 7 2 0 2 3 1 4 0 1 1 1

    Pkd 8 3 2 5 0 0 0 9 4 13 2

    Pkd 9 4 1 5 5 2 7 0 0 0 1

    Pkd 10 0 0 0 0 0 0 1 0 1 0

    Total 49 50 99 69 72 141 58 56 114 35

    Table 6.Number of House Sparrows recorded in the transects along Malappuram Road, Manjeri.

    Transect

    Name

    Count 1 Count 2 Count 3 Total

    nestsMale Female Total Male Female Total Male Female Total

    Mlp 1 15 11 26 27 13 40 43 26 69 6

    Mlp 2 2 3 5 3 4 7 3 4 7 1

    Mlp 3 11 4 15 10 6 16 14 11 25 3

    Mlp 4 9 4 13 12 6 18 6 7 13 1

    Mlp 5 0 0 0 0 0 0 0 0 0 0

    Mlp 6 12 5 17 13 6 19 27 14 41 7

    Mlp 7 1 0 1 4 6 10 0 0 0 0Mlp 8 5 4 9 5 6 11 4 2 6 0

    Mlp 9 1 0 1 0 0 0 1 1 2 0

    Mlp 10 0 0 0 0 0 0 0 0 0 0

    Total 56 31 87 74 47 121 98 65 163 18

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    Table 7.Number of House Sparrows recorded in the transects along Kozhikode Road, Manjeri.

    Transect

    Name

    Count 1 Count 2 Count 3 Total

    nestsMale Female Total Male Female Total Male Female Total

    Koz 1 5 2 7 7 4 11 8 3 11 4

    Koz 2 0 0 0 1 1 2 1 1 2 0

    Koz 3 6 2 8 7 9 16 6 4 10 2

    Koz 4 0 0 0 1 0 1 0 0 0 0

    Koz 5 2 1 3 3 4 7 3 0 3 3

    Koz 6 0 0 0 0 0 0 1 0 1 1

    Koz 7 0 0 0 0 0 0 1 0 1 1

    Koz 8 0 0 0 1 0 1 0 0 0 0

    Koz 9 1 0 1 0 0 0 0 0 0 0

    Koz 10 0 0 0 1 0 1 1 0 1 0

    Total 14 5 19 21 18 39 21 8 29 11

    3.2. Habitat factors and distribution of House Sparrows

    A summary of the habitat characteristics of transects surveyed is given in Table 8. All the

    transects except one had at least one building. About 73.3% (SD= 22%) of the buildings in the

    transects had cement-concrete roofs. Except three transects, majority of the buildings were built

    during the last 10 years and only few old buildings exist. All except two transects had shops with

    rolling shutter doors which is used by the sparrows for the nest placement.

    Of the 40 road-transects surveyed during this study, sparrows were found in all except

    two transects. However, the nests were not found in 16 transects. House Sparrow abundance and

    the number of nests in the road-transects were positively correlated to the numbers of buildings

    with cement-concrete roofs, rolling shutter doors, hotels and rice/cereal godowns. The number of

    nests was also positively associated with the number of grocery shops in the transects. The

    presence of vegetation in the transects had a negative correlation with the abundance of sparrows

    and the number of nests present (Table 9).

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    Table 8.Summary statistics of the habitat characteristics of the transects surveyed for the HouseSparrows in Manjeri Municipality, Kerala.

    Code Variable Mean SD Range

    NCRF No. of buildings with concrete roofs 5.502.74 0-11NTRF No. of buildings with tile roofs 1.881.56 0-7

    NSHTR No. of shutters 15.107.67 0-32

    NHTL No. of hotels 1.641.94 0-7

    NGCS No. of grocery shops 0.370.74 0-3

    NGDNS No. of godowns 0.130.34 0-1

    NWLS No. of wells 0.2549 0-2

    NWPS No. of water pipes 0.451.15 0-6

    NTREES No. of trees 2.052.55 0-9NGRASS No. of grass patches 0.700.79 0-2

    3.3. Nest site characteristics of the House Sparrow population at Manjeri

    Of the 109 nests recorded from the road transects and the market area during the study, 84 nests

    were studied in detail to reveal the nest site characteristics of House Sparrows. All the nests were

    placed in human-made structures in the buildings or artificial boxes and baskets established by

    the shop keepers (Plate 2). The nests are mainly constructed with straw, jute, packaging tapes

    (mostly thrown from the shops), feather, small pieces of grasses and several rubbish materials

    like cotton and plastic pieces.

    Majority of the nests (89.3%, n= 75) were placed above the roller shutter boxes followed

    by the artificial boxes provided by the shop keepers (4.8%), shelter boards in front of the shops

    (3.57%) and the ventilators (2.4%) (Figure 5). The nests were placed at an average of 3.831.29

    m above ground ranging from 2.5 6.3 m. The overall visibility of the nests was about 12.1%

    (10.6, range: 0-60%). The nests placed above the roller shutter boxes are well concealed underthe concrete shelters extending about 1.901.30 m (range: 0.5 6 m) above the nests. In general

    the nests were placed in the close vicinity of grocery shops, rice godowns and hotels (Table 10).

    The House sparrows in the market area placed their nests higher than their counterparts in the

    road-transects. The nests in the market were also close to hotels, vegetation cover and gardens

    (Table 11).

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    a b

    c d

    Plate 2. Nesting sites of House Sparrowsa. A pair of House sparrows in a nest on roller shutter box

    b.

    House sparrow nest in a card board boxc. House sparrow nest place on a board placed between the shutter boxesd. House sparrow nest in a bamboo basket

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    Table 9. Spearman rank correlation matrix for the habitat variables and the abundance of sparrows an

    Municipality, Kerala.

    VariablesConcrete

    roofs

    Tile

    roofs

    No. of

    ShuttersHotels

    Grocery

    ShopsGodowns Wells Pipes Trees

    Con. Roofs

    Tile roofs -0.072

    No. of Shutters 0.361* -0.044

    Hotels 0.557** -0.136 0.494**

    Grocery Shops 0.333* -0.064 0.249 0.548**

    Godowns 0.304* -0.061 0.263 0.404** 0.19Wells -0.077 -0.071 0.217 0.155 0.112 -0.027

    Pipes 0.123 0.053 0.202 0.205 0.132 0.13 0.418**

    Trees -0.561** -0.11 -0.585** -0.606** -0.454** -0.318* -0.022 -0.04

    Grass -0.627** 0.023 -0.555** -0.472** -0.287* -0.243 -0.189 -0.23 0.645*

    No. of Sparrows 0.347* 0.117 0.981** 0.491** 0.217 0.276* 0.195 0.19 -0.598*

    No. of Nests 0.435** 0.22 0.400** 0.551** 0.328* 0.307* 0.229 0.259 -0.543*

    * indicates a significant value atp< 0.05; **indicates a significant value atp< 0.01

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    Figure 5.Nest site use by House Sparrows at Manjeri Municipality, Kerala.

    Table 10.Nest site characteristics of House Sparrows in Manjeri Municipality.

    Code Variable Mean SD RangeHTGD Height from ground (m) 3.831.29 2.5-6.3

    VSNT Visibility of nest (%) 12.1410.56 0-60

    SHTR Shelter above nest (m) 1.901.30 0.5-6

    DNNT Distance from nearest nest (m) 7.6419.30 2-150

    DHTL Distance from nearest hotel (m) 26.2118.84 3-75

    DGWN Distance from nearest godown (m) 16.8826.37 1-125

    DGSH Distance from nearest grocery shop (m) 8.178.07 1-50

    DGAD Distance from nearest garden (m) 36.6917.95 8-100

    DVEG Distance from nearest vegetation (m) 37.0718.21 8-100

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    Table 11.Comparisons of the characteristics of House Sparrow nest sites in markets and road-side transects, in Manjeri Municipality.

    Code Variable Market(n = 31) Transect(n = 53)U p

    HTGD Height from ground (m) 4.120.20 3.330.14 538 0.001

    VSNT Visibility of nest (%) 10.851.03 14.352.56 814 0.942

    SHTR Shelter above nest (m) 1.940.19 1.820.20 814 0.941

    DNNT Distance from nearest nest (m) 9.343.31 4.740.53 749 0.490

    DHTL Distance from nearest hotel (m) 18.0911.23 40.1021.15 346 0.001

    DGWN Distance from nearest godown (m) 21.514.34 8.971.75 587.5 0.029

    DGSH Distance from nearest grocery shop (m) 8.581.07 7.451.54 647 0.104DGAD Distance from nearest garden (m) 30.812.32 46.742.74 361 0.001

    DVEG Distance from nearest vegetation (m) 30.662.33 48.032.68 330 0.001

    4. DISCUSSION AND CONCLUSION

    The present study shows that the core area of the Manjeri, a fast growing medium size

    town supports a large population of House Sparrows. We have no historical data on the status of

    House Sparrows in Manjeri and the surrounding areas; therefore we do not know whether the

    House Sparrow numbers changed drastically over time. However, there seems to be indications

    of population changes in the first three transects in the Pandikkad Road (Pkd 1 -3), where about

    180 (96 males and 84 females) sparrows were counted during January 2002 (P. Balakrishnan,

    Unpublished data). During the present study only 82 individuals were counted from these

    transects. We did not attempted to calculate the sex ratio of the species as we may have missed

    several incubating female sparrows during our surveys.

    The buildings with concrete roofs and rolling-shutter doors provided excellent nesting

    sites for the House Sparrows. Those shutters constructed with a gap between the roller box and

    roof of the buildings supported the sparrow nests, while in many cases the roller box is attached

    very close to the roof which cannot accommodate the nests. Sparrows also used some of the

    artificial nesting sites like card-board boxes or bamboo baskets provided by the shop keepers.

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    This indicates the adaptive nature of the species to new environments. However, the more

    recently built shopping centres with glass facades (exterior construction of the buildings) do not

    provide much space for placing the nests. Thus the development of modern buildings is going to

    be major threat to the breeding sparrows in the near future. A loss of suitable nesting sites in

    modern buildings or after renovation and an insufficient nestling diet are discussed as main

    causes for the decline of sparrows in urban areas, but other factors may also play a role

    (Summers-Smith 2003, Vincent 2005). Although the vegetation cover in the transects are very

    low, there is a considerable amount of small trees, shrubs and small gardens outside the transects,

    which may host enough insects for feeding the nestlings. Most of the House Sparrow nests were

    placed at about 4 m height. Indykiewicz (1990) found that the most common height when

    analysing the location of urban sparrow nests was between three and four metres high. The

    domestic cats and owls appear to be potential predators of the House Sparrow nests.

    The level of pollution is and its impact on the sparrows was not documented in this study.

    However, as the density of vehicles is very high at Manjeri it may have some potential impact on

    the species. Recently there have been several studies supporting the notion that long-term

    exposure to higher levels of radiation negatively affects the abundance or behavior of House

    Sparrows (Balmori and Hallberg. 2007; Everaert and Bauwens, 2007). There are about 41 mobile

    phone masts in the 3 km vicinity of the Manjeri town. The impact of the radiation from these

    mast need to be studied soon.

    In conclusion, the present study indicates that Manjeri host a considerably good population of

    House Sparrows and the survival of the species depends on the protection of similar populations

    in small towns by minimizing the pollution levels, use of pesticides and protection of old

    buildings and construction of sparrow friendly buildings in the future.

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