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110<br />
Other parameters meaeured included water and air temperatures and<br />
general observations concerning rainf a11..<br />
Survey5 llere initiated approximately one hour aftetr sunset utilizing<br />
either a motorized five n. alutniniu{n boat or three to five m. dugout canoes.<br />
Animal5 were spotted with a 2OO OOO candlepower liqht and recorded by .3<br />
m <strong>size</strong> classes. lrlhen species could not be deterfiined, animats were placed<br />
into an unknown category by <strong>size</strong> class. These anjJnal6 were added to known<br />
sp€cieE c(fuhts in the sane proportion that the known animals were<br />
obEerved. Additionally, broader <strong>size</strong> claEses were estabtished for those<br />
anirnals h,hich could not be <strong>size</strong>d accurately.<br />
Even though we had beqinning, inter_ftediate and eoding points of the<br />
najority of the routes our lack ot a good map/photograph prevenEeo an<br />
exact determination of transect length, But in ord€r to establish an<br />
approximate length of each ror.rte, we calcslated the distance betr,een<br />
begi.rning, intermediate and ending points.<br />
Also! f-ive immature black caiman were captLrredr fieasured and<br />
rFleased and one adult termale black caiman r,las ceptured in a Mlrrphy trap,<br />
measured, and released. lvleasurements were algo obtajned frofi tLlo animalg<br />
taken for thejr abdominal fat, by a local fiEherman. Primarily, these a.i.nals<br />
were measurec, to Verify our <strong>size</strong> clessifications,<br />
In addition, we initiated pffortq to acquire LANDSAT photogrcphs of<br />
the study area to aid in the asseesment of habitat. These nawe oeen<br />
purchased but have not been received.<br />
Results<br />
During the 13 daye ot the survey, }le inspect€,d lagoons and other<br />
cairnan habitat alonq approxi$ately 24O km ol the Ris Napo and Rio Lagarto<br />
Cocha. hle established 1? separate slrrvey roLrtes and conducted at least<br />
one niqht light gurvey along each route.<br />
BeEauEe the variation inherent in ni.ght light counts cannct b€,<br />
quantified when only one survey is conducted the data presented here are<br />
of lirnited value. Ho|reveri $re are presentty in the process oJ replicating<br />
the counts on a monthly basiE to quantity annuat variation .in number5 of<br />
caiman obEerved. But until those data are analyzed we nuEt rely on the<br />
survey results as they are to provic,€' some preliminary insights into<br />
DoFulation status,'<br />
Crocodilians *ere observad along all 12 survey routes and black<br />
cairnan |,,ere observed in sone proportion along every route pxcept one. The<br />
variation in the ratio ot It. nioer to Caiman crocodi]us is not readily<br />
explainable by obvious habitat differenceg, But it ranged fro|||.OO to !.OO<br />
of the total nuober observed bejnq identified as ft. nioer (Table I).<br />
Of the en-imals <strong>size</strong>d, 627. were I.8 n or smaller, most of l.Jhich probably<br />
represent the sub-adult <strong>size</strong> classr tth-iJ.e 272 fell into the LA to 2.7 m<br />
class and 9Z were the very large anjmals (qreater than 2.7 .n)(Fig, 1). Even<br />
though 24 hatchlings grere observed the fact r.re r4ere unable to access<br />
areas that appreared to be good proctuction habitat probably<br />
sj.gnificant under-estimate of the proportion of hatchljnos in the<br />
ooDulation.<br />
A signiJicant proportion c|t the habitets surveypd |rere surrolrnc,ec,<br />
by flooded torest./heavy cover .naking observab_ili.ty a problem. AlEo, there<br />
lJere some population6 that appeared to be ,'luch more *ary than others<br />
suggesting that hunan ectivity tnay cause behavioral changes which will<br />
atfect observabilitv.