Breeding Bird Survey Results 2007                          Stoller-ESER-111

SUMMARY

The results from the 2007 INL BBS were similar to previous years where shrub-steppe and grassland bird species dominated the observations. The total bird observations (n = 5412) and species richness (n = 69) from all routes is above the INL average since 1985. Following common patterns of abundance from previous INL BBS, horned larks were the most abundant species followed by western meadowlark, Brewer’s sparrow, sage sparrow, and sage thrasher. These five species are continually among the most abundant detected during these surveys, and considering that these species are declining in other parts of their range, the habitat quality on the INL appears to remains high. Four species (greater scaup, bald eagle, osprey, and turkey vulture) were recorded for the first time during this year’s survey. The INL continues to support species of special concern and this year six species (greater sage-grouse, ferruginous hawk, long-billed curlew, Franklin’s gull, Brewer’s sparrow, and grasshopper sparrow) listed by the State of Idaho as imperiled or critically imperiled were documented on site.

Future Data Analysis

With over two decades of BBS data, long-term INL-specific species trend analysis should be conducted for each species. Past reports have provided details regarding particular species, but no effort has been made to consider a comprehensive analysis of all BBS observation data from the INL. Before the complete dataset can be analyzed, all of the data have to be organized into a single database. Since the INL BBS surveys have been conducted by different organizations since 1985, database formats and file naming conventions vary. We will be organizing all INL BBS during 2008 to facilitate a more in depth analysis to be included in next year’s report.

Landscape Change and Habitat Variation

The habitat and vegetation communities across the INL are a diverse mosaic of sagebrush-steppe habitat. The INL has experienced some large natural disturbances (e.g. wildfire) which have caused changes in vegetation community composition and distribution across the site. It is not well understood how bird populations respond to alterations of habitat composition and distribution across the landscape (Knick and Rotenberry 2002), and habitat fragmentation can influence local population dynamics. Local bird populations and community assemblages can show a response to these habitat changes, and the long-term BBS data should reflect these changes. We will investigate the patterns of habitat change in conjunction with changes in observed bird abundance and richness along routes.

LONG-TERM COMMUNITY DIVERSITY TREND

Diversity indices have not been calculated each year and a useful comparison would be to calculate Shannon’s H and EH for all BBS routes from all years to assess which routes have experience significant change in bird community abundance. The initial community diversity results reported above consider community differences between different routes in the same year. It is unknown how diversity on the same route has changed over time. A number of community similarity indices, such as Morisita’s index (Morisita 1959) or percent similarity, can be calculated to address this question. We anticipate coupling the results from the spatial analysis described above with the results from community diversity change over time to present a comprehensive description of how bird communities have changed on the INL since 1985.

ACKNOWLEDGEMENTS

We would like to thank Sue Vilord for conducting the surveys this year and providing training and suggestions for future INL BBS. We also thank Neil Hukari (NOAA/ARLFRD) for providing the weather data summaries from the CFA.

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