Dataset 337

Mountain Birdwatch

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Realm: Terrestrial
Climate: Temperate
Biome: Temperate broadleaf and mixed forests
Central latitude: 44.250000
Central longitude: -72.187500
Duration: 11 years, from 2000 to 2010

763 records

87 distinct species

Across the time series Troglodytes hiemalis is the most frequently occurring species

Methods

Surveys were conducted under acceptable weather conditions (no precipitation temperature >2 ?C wind speed <32 km/h) from 1 to 28 June. Surveys were conducted between 04:30 and 08:00 EDT and most were completed by 06:30 EDT. Observers listened quietly for ten minutes at each of five stations. [In 2003 we increased the 5-species point count length from five to ten minutes in order to gather more information and to achieve methodological consistency with the all-species protocols and with Canada?s High-Elevation Landbird Program.]They recorded the number of each focal species seen or heard during three time periods: 0-3 minutes 3-5 minutes and 5-10 minutes. If Bicknell?s Thrush was not detected during or between point counts surveyors returned to each point immediately after the full route survey and broadcast a one-minute recording of the bird?s vocalizations in order to elicit a response from present but silent birds. A two-minute listening period followed each broadcast. [Prior to 2003 the broadcast duration was three minutes.]Audio playbacks were discontinued upon detection of one or more individuals. If no Bicknell?s Thrush responded to the broadcasts the status of the species at that location was classified as unknown. Monitors who completed their surveys without encountering Bicknell?sThrush were asked to conduct follow-up audio playback surveys at dusk or dawn before 15 July (after Atwood et al. 1996). If no observations of Bicknell?s Thrush were made during the second visit the species was presumed to be absent from that site. Site selection was based on a GIS model of potential Bicknell?s Thrush habitat that incorporates elevation. latitude. and forest type (see Lambert et al. 2005). The model depicts conifer-dominated forests above an elevation threshold that drops 81.63 m for every one-degree increase in latitude (-81.63 m/1? latitude). The threshold?s slope corresponds closely with the latitude-elevation relationship for treeline in the Appalachian Mountain chain. which is -83 m/1? latitude (Cogbill and White 1991). Four routes have been established on peaks lying below the elevation threshold. while forty routes cross the threshold due to the limited availability of trails or land area above the threshold. We made an attempt to randomize site selection by randomly assigning priority ranks to discrete units of high-elevation habitat. However. the choice of sites was constrained by the availability of volunteers and the location of existing trails. When placing routes. we favored discrete starting points (e.g. trail junction). extensive conifer stands. and upper elevations. Volunteers establishing a route for the first time placed five points at 200- to 250-m intervals along a mapped course. Monitors submitted a detailed description of each station in order to facilitate its location in future years. 10% quinaldine solution spread throughout the study site to anesthertize fish. Samples were then collected by hand or using dip nets. Rocks and boulders overturned and replaced with minimal disturbance. observation surveys conducted under acceptable weather conditions Unit of abundance = Presence, Unit of biomass = NA

Citation(s)

Vermont Center for Ecostudies, Lambert, J. D. & Hart, J. (2015) “Mountain Birdwatch 1.0”. KNB Data Repository, 10.5063/F1DN430G, accessed 2016.