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Methods - Michigan Breeding Bird Atlas Website

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<strong>Methods</strong><br />

The Second <strong>Michigan</strong> <strong>Breeding</strong> <strong>Bird</strong> <strong>Atlas</strong><br />

chosen as priority blocks; in the NLP, two of the four blocks in a township were<br />

randomly selected; and only one block was randomly selected in the UP. These decisions<br />

were based primarily on the availability of volunteers in the different regions of the state.<br />

Because of the difficulty of achieving coverage goals in MBBA I, fewer priority blocks<br />

were used in MBBA II: A single priority block was chosen in each township, regardless<br />

of the region. To facilitate comparisons between the <strong>Atlas</strong> projects, the MBBA II priority<br />

blocks are a subset of those used in MBBA I. Therefore, while a priority block was<br />

randomly selected out of the four possibilities per township in the SLP, there were only<br />

two possibilities per township in the NLP and one possibility per township in the UP. A<br />

secondary block was selected in each township for MBBA II in roughly the same fashion.<br />

Observers were directed to survey the priority blocks first. If they were unable to travel<br />

to a more distant priority block, the secondary and non-priority blocks could be surveyed.<br />

Thus, data from all blocks were accepted, regardless of priority status, with the additional<br />

coverage expanding our knowledge of species-specific distributions. Because block<br />

coverage was unequal in MBBA II and MBBA I, results have been compiled by township<br />

to facilitate comparisons within and between <strong>Atlas</strong>es.<br />

Coverage Goals<br />

A major objective of the field work portion of MBBA II was to adequately cover each<br />

priority block. As in MBBA I, a minimum count of 50 species was used to signify an<br />

adequate level of coverage (McPeek and Adams 1991). This was an internal quality<br />

control measure and surveys were never cut short at this number. While blocks in some<br />

habitats (urban centers, agricultural areas, and deep forest) might not reach 50 species,<br />

this measurement was useful in identifying locations in need of additional coverage. In<br />

addition to number of species, coverage can be described by field hours (effort) and by<br />

the number of records obtained. While these metrics had no defined goal, they provide a<br />

useful summary of coverage information for MBBA II. The standard <strong>Atlas</strong> forms are the<br />

casual card, the point count form, and the survey checklist form. Effort was collected on<br />

two forms: The point count protocol stipulated that observers spend five minutes at each<br />

point, so a standard 25-point survey counted as approximately two hours, while the<br />

survey checklist asked for hours spent in the field. Each species listed on a form was<br />

considered a record.<br />

While effort seems a very straightforward measurement, the number of hours needed to<br />

cover a block varies with the skill of the individual observer. How observers recorded<br />

and perceived their time spent in a block also varied. Surveys from volunteers which did<br />

not include time were assigned field hours at the rate of one hour per 30 species reported.<br />

Because data on hours were not available from MBBA I, no comparisons can be made in<br />

terms of hours of effort with MBBA II.<br />

© 2012 Kalamazoo Nature Center<br />

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