The use of distance sampling for estimating desert tortoise populations
is briefly reviewed and forms a foundation for the current study.
Data for this study was obtained from the eight 9 km2 study plots
in the southern Mojave Desert established at Marine Corps Air
Ground Combat Center and Joshua Tree National Park in 1995. An
experimental design was developed to sample live tortoises, carcasses,
burrows, and scats using distance sampling as the population (in
the statistical sense) estimator. Tortoise, burrow, and scat
densities were estimated at nested multiple-scales to produce
an unbiased desert tortoise distribution/density surface for the
landscape. This analysis and protocol was presented at the Desert
Tortoise Council Symposium in 1997. The experimental design and
resulting database provided an opportunity to directly compare
distance sampling and strip transects of varying widths for estimating
burrow and scat densities on landscape scales at plots that varied
enormously in desert tortoise abundance. The tested hypothesis
was: Tortoise sign density estimates using distance sampling should
be independent of and indeed similar at any surveyed band width;
while wide strip transects should underestimate tortoise sign
density, because all sign within the transect are not detected
by the surveyor. However, as strip transect widths approach the
detection function parameter calculated from distance sampling,
the two methods should yield comparable results. The optimal
strip transect width for estimating scat densities should be much
narrower than the corresponding transect band for burrows, because
scats are much more difficult to observe than burrows. The data
strongly and unequivocally support the posed hypothesis. Distance
sampling is time intensive because the perpendicular distance
between each located object and an established line transect must
be accurately measured. The data from my protocol suggest that
distance sampling need only be used on actual tortoises. Tortoise
sign densities can be adequately estimated from strip transects
whose optimal widths are separately calculated for burrows and
scats from an initial pilot study using distance sampling. This
pilot study is necessary, because optimal strip transect width
is habitat and to some extent year specific. For example, in
a highly productive year the increase in vegetation and litter
would require narrower strip transects for burrows and scats.