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Vascular Plant and Vertebrate Inventory of Saguaro ... - USGS

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during which time we assigned all birds seen<br />

<strong>and</strong>/or heard into one <strong>of</strong> the following distance<br />

categories: ≤ 100 m, > 100 m, or “flyover.”<br />

When possible, we noted the sex <strong>and</strong> age class <strong>of</strong><br />

birds. We recorded birds observed before or after<br />

surveys as “incidentals” (see section below) <strong>and</strong><br />

we did not use techniques to attract birds (e.g.,<br />

“pishing”).<br />

Effort<br />

The number <strong>of</strong> sections along each transect<br />

ranged from eight to 13 (Table 5.2). We surveyed<br />

each transect four times in the winter <strong>of</strong> 2002 <strong>and</strong><br />

2003.<br />

Analysis<br />

Due to the low number <strong>of</strong> observations<br />

within 100 m <strong>of</strong> the transect lines, we used<br />

all observations (except unknown species) to<br />

estimate relative abundance (see Methods section<br />

<strong>of</strong> VCP surveys for more details).<br />

Nocturnal Surveys<br />

Field Methods<br />

To survey for owls we broadcast commercially<br />

available vocalizations (Colver et al. 1999) using<br />

a compact disc player <strong>and</strong> broadcaster (Bibby et<br />

al. 2002) <strong>and</strong> recorded other nocturnal species<br />

(nighthawks <strong>and</strong> poorwills) when observed. We<br />

established nine transects (Fig. 5.2). The number<br />

<strong>of</strong> transects per elevation stratum was lowest<br />

for the middle elevation (n = 2) <strong>and</strong> highest for<br />

the high elevation areas (n = 4) (Table 5.2). The<br />

number <strong>of</strong> stations per transect varied depending<br />

on logistical constraints but all stations were a<br />

minimum <strong>of</strong> 500 m apart. For transects that we<br />

visited multiple times, we attempted to reduce<br />

sampling biases by varying direction <strong>of</strong> travel<br />

along transects. We began surveys approximately<br />

45 minutes after sunset.<br />

We began surveys at each station with a<br />

three-minute “passive” listening period during<br />

which time we broadcast no calls. We then<br />

broadcast vocalizations for a series <strong>of</strong> two-minute<br />

“active” periods. We broadcast vocalizations<br />

<strong>of</strong> species that we suspected might be present,<br />

based on habitat <strong>and</strong> range information. The<br />

species that we broadcasted changed based on the<br />

elevation stratum <strong>of</strong> the surveys:<br />

51<br />

• Low elevation: elf, western screech,<br />

burrowing, <strong>and</strong> barn owls;<br />

• Middle elevation: elf, northern pygmy,<br />

flammulated, <strong>and</strong> whiskered screech<br />

owls;<br />

• High elevation: northern pygmy,<br />

flammulated, northern saw-whet, <strong>and</strong><br />

whiskered screech owls.<br />

We excluded the great horned owl from the<br />

broadcast sequence because <strong>of</strong> its aggressive<br />

behavior toward other owls (though we recorded<br />

them incidentally). Also, we did not survey for<br />

the Mexican spotted owl or the cactus ferruginous<br />

pygmy-owl because that would have required<br />

use <strong>of</strong> specific protocols <strong>and</strong> because park staff<br />

survey periodically for these species.<br />

We broadcast recordings <strong>of</strong> owls in<br />

sequence <strong>of</strong> species size, from smallest to largest,<br />

so that smaller species would not be inhibited by<br />

the “presence” <strong>of</strong> larger predators or competitors<br />

(Fuller <strong>and</strong> Mosher 1987). During active periods,<br />

we broadcast owl vocalizations for 30 seconds<br />

followed by a 30-second listening period. This<br />

pattern was repeated two times for each species.<br />

During the count period we used a flashlight to<br />

scan nearby vegetation <strong>and</strong> structures for visual<br />

detections. If we observed a bird during the<br />

three-minute passive period, we recorded the<br />

minute <strong>of</strong> the passive period in which the bird<br />

was first observed, the type <strong>of</strong> detection (aural,<br />

visual or both), <strong>and</strong> the distance to the bird. If a<br />

bird was observed during any <strong>of</strong> the two-minute<br />

active periods, we recorded in which interval(s)<br />

it was detected <strong>and</strong> the type <strong>of</strong> detection<br />

(aural, visual, or both). As with other survey<br />

methods, we attempted to avoid double-counting<br />

individuals recorded at previous stations. We<br />

also attempted to use a different observer for each<br />

visit, alternate direction <strong>of</strong> travel along transects,<br />

<strong>and</strong> not survey during inclement weather.<br />

Effort<br />

The number <strong>of</strong> stations <strong>and</strong> visits to each transect<br />

differed among transects (Table 5.2). Although<br />

we had the most transects in the high elevation<br />

stratum, we had most (56%) <strong>of</strong> our survey effort<br />

in the low elevation stratum because <strong>of</strong> greater<br />

ease <strong>of</strong> accessing stations.

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