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Ecological and anthropogenic covariates ... - GANGAPEDIA

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correction factor for the float measurements to convert these into stream velocity was<br />

determined from simultaneous flow meter readings.<br />

I recorded depth <strong>and</strong> width, along with GPS locations, at 0.5 km intervals along the<br />

length of the river <strong>and</strong> at 10 m intervals along the channel width at each of these 0.5<br />

km intervals. Air <strong>and</strong> water temperatures were recorded at 30 minute intervals using<br />

data loggers (HOBO Pendant Temperature Data Loggers - Part # UA-001-XX). Air<br />

temperatures were also collected from the National Informatics Centre<br />

(weather.nic.in/). Shoreline substratum was classified broadly into clay-loam, s<strong>and</strong>,<br />

gravel <strong>and</strong> s<strong>and</strong>stone-rock, based on st<strong>and</strong>ard soil texture tests. Presence of<br />

confluences, s<strong>and</strong> <strong>and</strong> spit bars, <strong>and</strong> mid-channel isl<strong>and</strong>s was recorded.<br />

Anthropogenic activities like s<strong>and</strong> mining, fishing, bankside cultivation, livestock<br />

presence, river crossing <strong>and</strong> miscellaneous activities (bathing, washing, defecation,<br />

grass soaking, temple fairs, etc) were recorded for each of the 2.5 km segments at a<br />

scale of 0.5 km (See Table 2).<br />

While the number of people, vehicles <strong>and</strong> livestock involved in each type of activity<br />

were recorded, only data on the extent of each activity type was analysed since this<br />

factor seemed to have greater influence on gharial distribution as compared to the<br />

number of people/ vehicles/ livestock per unit area.<br />

14

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