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In general, native species diversity / abundance and overall forest health drop significantly with
increasing deer herd size. An often cited research project that provides quantitative guidance on deer
population levels associated with ecological damage was performed by David deCalesta, based at the USForest Service in Pennsylvania (deCalesta 1994, deCalesta 1997).
Over the course of a 10-year studyusing forest enclosures with known densities of deer, deCalesta determined that native forest herbs and tree seedlings became less abundant with deer densities between 10 and 20 per square mile.
At densities exceeding 20 per square mile, palatable native plant species disappear and forest shrub-nesting song birdsdrop in abundance with the loss of the shrub layer.
Starvation of deer occurred when densities exceeded 65 per square mile.
This study suggests that deer densities exceeding 10 per square mile have negative ecological impacts (Note: Independent historical studies determined that pre-European colonization deerdensities were approximately 10 per square mile and breakage – McCabe and McCabe 1984 and breakage of the Lyme disease transmission cycle may occur at 8 deer per square mile – Stafford 2007).
Numerous studies and reviews have been conducted on the impacts of white-tailed deer on forest
ecosystems. A comprehensive review was conducted in Pennsylvania (Latham et al. 2005,
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