public read Forest Ecosystem Monitoring Cooperative

705 Spear StreetSouth BurlingtonVermont05403United States of America

(802) 656-0683femc@uvm.eduwww.uvm.edu/femcTeatown Lake Reservation leadAll trees (> 10 cm dbh; > 1.4 m height) and saplings (< 10> 1.4 m height) within the outer plot were counted, marked, identified to species, status (live or dead) noted and dbh (cm) recorded in the tree table section of the forest plot data sheets. Approximate canopy dieback was also estimated for each live tree or sapling using the following scale: < 5>95%. Shrubs (> 1.4 m height) were counted, marked, identified to species and status noted. Only shrubs that contribute significantly to the midstory canopy are included. They are listed in Table 2.Forest Ecosystem Monitoring CooperativeVickyKellycontentProviderDanielleBegley-MillerprincipalInvestigatorUpland deciduous forest is the most common habitat type at Teatown. The most common species that dominate Teatown’s forests to create various natural communities are oak, hickory, maple, beech, birch, and tulip poplar. The forests of northern Westchester County and throughout much of the northeast are threatened by numerous factors including overabundant deer, invasive species, climate change and development. While these issues are often connected such that one may occur or worsen because of the presence of another, overabundant deer are considered the greatest current threat to the forest ecosystem. White-tailed deer overabundance has been extensively studied at Teatown since 2009. A healthy forest, defined as one with a dense understory of native trees and shrubs, is necessary for the forest to continue thriving into the future and to support all organisms within it. Anecdotal observations of loss of the understory started in the 1980s. To address the forest health issues, Teatown initiated a deer management program in 2014 and has an invasive management plan. To understand the success of our management programs and to determine if other management activities are needed, forest monitoring of forest plots was initiated in 2015 and is ongoing.Teatown Forest Inventory, Forest Plot Data, Tree DataAll trees (> 10 cm dbh; > 1.4 m height) and saplings (< 10> 1.4 m height) within the outer plot were counted, marked, identified to species, status (live or dead) noted and dbh (cm) recorded in the tree table section of the forest plot data sheets. Approximate canopy dieback was also estimated for each live tree or sapling using the following scale: < 5>95%. Shrubs (> 1.4 m height) were counted, marked, identified to species and status noted. Only shrubs that contribute significantly to the midstory canopy are included. They are listed in Table 2.VMC.1767.3897mySQL/femc/data/archive/project/teatown-lake-reservation-forest-plot-monitoring/dataset/teatown-forest-inventory-forest-plot-data-12015-08-19YearYearNo description for this attributeintmeter-1DateDateNo description for this attributedateD-M-YYPlotPlot NumberNo description for this attributeintmeter-1TagTag IDNo description for this attributetextSpeciesSpeciesNo description for this attributetextStatusStatus, Live or DeadNo description for this attributetextDBH_cmDiameter at Breast HeightNo description for this attributedecimalmeter-1Dieback_percentDieback percentNo description for this attributetextStem_Class_cmStem ClassNo description for this attributetextSize_Class_cmSize ClassNo description for this attributetextNotesNotesNo description for this attributetext