# Chapter 5 Density Estimates of Malabar Giant Squirrel in the Study Area

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## Density Estimates of Malabar Giant Squirrel in the Study Area

5.1 Determination of Multiplier
Density estimation was carried out based on distance data of giant sightings collected during the survey. Of the total 160 giant squirrel sightings, 90 were recorded from Bhimashankar Range 1 alone. Apart from higher abundance in Bhimashankar, the sampling intensity was also much higher in this range compared to the survey in the remaining areas. It was therefore decided to carry out the density analysis separately in Bhima1 Range and the rest of the study area.
Giant squirrels are much more active during the morning hours and evening hours (peak hours) with a lull in the middle of the day (off-peak hours). Therefore sampling should ideally be carried out in the peak hours when the giant squirrels are most active. However, in the present survey, it was not possible to restrict sampling only to peak hours and survey was carried out at peak as well as off-peak hours depending on the trail location and the logistics of reaching the trail.
A basic assumption of line transect surveys is that all squirrels are “available” for sampling. This is the case during the peak hours. However, during the off-peak hours some giant squirrels retire to their nests and are “not available” for sampling. This is the case only for a percentage of squirrels. This is contrary to the basic assumption that all squirrels are available for survey. Conventional distance sampling assumes that g(0)=1 on the sampling line. However, in the present situation g(0) is less than 1 in off-peak hours because of some squirrels not being available for sampling. A correction factor needs to be applied to the density estimate known as a multiplier. The multiplier is usually determined by a separate experiment.
Since the sightings made at Bhimashankar Range 1 were made in the same location and we had substantial number of sightings these were used to determine the multiplier.
We divided the sightings made at Bhimashankar into sightings made during peak hours and those made during off-peak hours. Peak hours were considered as the time before 11 am and after 4 pm during winter. In summer peak hours were considered as the time before 10 am and after 5 pm. The interval in between was considered as off-peak hours (Renee Borges, pers. comm.). The length of each trail was also divided into length sampled during peak hours and length during off-peak hours. In this manner the entire data for Bhimashankar Range 1 was segregated into two sets consisting of data collected during peak hours and data collected during off-peak hours. The encounter rates were determined for both these data sets as follows:
Repeal = Number of sightings during peak hours

Effort during peak hours

Ruff-peak = Number of sightings made during off-peak hours

Effort during off-peak hours

Table 5.1: Encounter Rates (n/l) during peak and off-peak hours in Bhimashankar Sanctuary

 Description Total Peak Hours Off-peak hours No. of trails 54 37 37 No. of Encounters 100 52 38 Effort 186.78 78.31 108.47 Encounter Rate 0.8812 0.5059 Standard Error 0.216 0.165

The encounter rates at peak and off-peak hours would have been the same if the giant squirrels were active throughout the day. However since they are less active during the off-peak the encounter rates during these hours is lower than the peak hours. The ratio of the two encounter rates reflects the ratio of giant squirrels that is available during off-peak hours to those available during peak hours. Therefore the multiplier is calculated as:

M = Ruff-peak = 0.5059 = 0.5741

Repeal 0.8812

5.2 Density of Giant Squirrels in the Study Area
The analysis was carried out in Distance 6.0 Release 2. As stated earlier we defined two sets of data, each with their own sets of trails as shown in Table __. The off-peak trails need to be assigned the above multiplier so that the density estimate based on these trails is increased to reflect the number of giant squirrels that is not available for sampling. However the present version of Distance allows assignment of multipliers only at the Global layer and not at the transect layer. To circumvent this limitation the effort for off-peak lengths of all transects was multiplied by the above multiplier. This has the effect of reducing the transect length of the trails during off-peak hours thereby increasing the density to account for the unavailable giant squirrels.
The density estimation parameters for Bhima 1 are given in Table 5.1 and the density estimation parameters for the rest of the study area is given in Table 5.2.
Table 5.2: Density of Giant Squirrel in Bhimashankar Range 1

 Value Total Peak Off-peak Number of Trails 63 55 53 Encounters 86 52 38 Number of Giant Squirrels 97 61 40 Effort 186.8 78.3 108.5 Effort (corrected) 140.6 78.3 62.3 Max strip half width (m) 42 m Truncated strip half width (m) 30 m Average cluster size 1.126 Selected Model Uniform with polynomial correction Density 15.89/sq.km. (11.00-22.74) %CV 18.29 %

Table 5.3: Density of Giant Squirrel in Rest of Study Area (Other than Bhimashankar)

 Item Value Total Peak Off-peak Number of Trails 191 123 146 Encounters 43 29 24 Number of Giant Squirrels 55 31 24 Effort 538.6 206.3 332.3 Effort (corrected) 397.1 206.3 190.8 Max strip half width (m) 55 m Truncated strip half width (m) 40 m Mean cluster size 1.037 Model Uniform with cosine correction Density 2.92/sq.km. (1.95-4.43) %CV 15.82%

The density estimate for Bhimashankar is quite high at 15.89 /km2while the average density of giant squirrel in the rest of the study area is 2.92/km2.
Estimation of number of giant squirrel requires estimation of giant squirrel habitat in the sampled area. This is a complex exercise and involves interpretation of satellite imagery. It was not possible within the time and resources available to us. Hence estimation of giant squirrel numbers was not carried out. However this is a feasible exercise and may be attempted in the future.

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