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80<br />
Sustainablc harvcsls were calculaled by rsking what level of change in I, or m, would convert an<br />
ircreasing populaiion to a slaiionary one, i.e. would mnkc c'= l Equation I is thcn solved for lhe new<br />
parameter value, for example, fof egg harvests, wherc q is lhe proporiion ofeggs collected, m. in equation<br />
I becomes (l 'q)m. at equilibrium, reananging thc equalion then gives:<br />
\-r<br />
n<br />
(craig 9! 4!. 1992).<br />
RT]SUI,TS AND DISCUSSION<br />
Given lhe pammeler values of Table 1, the polential rate of incrci$e for Nile crocodiles was estimatcd lo<br />
be e'= 1.08, i.e. an 87, annual rate of incre.se. Unceilxirly in the parametea used. however. result in<br />
npproximate conficence linits of e' = 1.03 lo e' = 1,13.<br />
The vast majority of uncert:inty (Column 4 of Table 1) in lhe value of c' appears to derive from pmr<br />
cslimatcs of three piuamctcn, namcly survivorship Io age l. survivorship from 1 lo maturily and ag€ at<br />
maturily. ClcaJly, if lhere is to bc ar improvement in otu ability lo make prediclions, future res€lrch must<br />
concentrale on obhining beller estimates of lhcse.<br />
Susmined yields of a variety of harvesling slralegieshow that egg collcclion xnd reffing to a <strong>size</strong> of 12<br />
melres is superior to any other sIrxtegy. e.g. Txble 2 compares the yie,d o[ egg collection with crcpping<br />
animals lrom lhc wild direclly for skin.<br />
Table 2. Comparison of egg collection wilh cropping animals >1,2 metres<br />
STRATDCY<br />
SUSTAINABLE<br />
% TAKFN<br />
9t%<br />
SKIN YIELD<br />
218<br />
There may be less differential economically between the slrategies of Table 2, because of the cost of<br />
hxrhing and rearing crocodiles. but in cons€rvalion terms. it is the absolute compxrison which is valid.<br />
The robustness ofegg collcction as a slralegy is also obvious from lhc pcrccnlagc of eggs it is permissible<br />
to collect. Such a high proportion collected would be unlikely to be achieved evcn if lhere were no<br />
restrictions on egg collection. This robushess bsromes even mo.e apparent when options involving<br />
replacement of juvcniles are investigated. Here the relum of 0,5% (of lhe number of collected eggs) as<br />
crocodiles rearcd to the length of l.2m resulls in reslonlion of sustainabilily even when all eggs are<br />
collecred (Gaig 9! 4., 1992).<br />
The simple model of crocodllc population dynamics describcd here enables somo useful conclusions to<br />
be drawn about safe harvesting slrategies. That these also seem inluilively acceptcbl€ is additionally<br />
encouraging.