Maintaining a Healthy Sugarbush
Maple producers benefit from spending time, and maybe some money, ensuring they have a healthy and productive sugarbush.
Showing 31 – 40 of 107 resources
Maple producers benefit from spending time, and maybe some money, ensuring they have a healthy and productive sugarbush.
Relatively little work has been conducted investigating trends and influences of the annual growth of sugar maple trees, utilizing the widths of tree rings to estimate growth rates for each year. Using this tree-ring approach, recent research suggests that growth rates have been decreasing in the Adirondack Mountains of New York State.
The amount of sap that can be extracted annually from trees for maple syrup production using current equipment and practices is more than double the typical yields achievable when current maple industry tapping guidelines were developed. The growth rates of trees tapped with these Òhigh-yieldÓ practices at 18 sites in Vermont were measured and evaluated to determine whether they were sufficient for the replenishment of conductive wood to remain at sustainable levels when current tapping guidelines are followed.
Recent technological advancements have increased the amount of sugar-enriched sap that can be extracted from sugar maple (Acer saccharum). This pilot study quantified overall sugar removal and the impacts of vacuum (60 cm Hg) and gravity sap extraction on residual nonstructural carbohydrate (NSC) concentrations and on stem and twig growth.
We found significant populations of snake worms devouring the organic matter, causing soil conditions that discouraged growth of understory native plant species. We are looking at their distribution in maple stands throughout the region relative to forest management practices, and assessing their impact on understory diversity, maple regeneration and various soil characteristics.
Steve Childs, the NYS Maple Specialist at Cornell Maple located in Ithaca, NY discusses extreme weather, climate variability, and adaptations taken to overcome weather challenges.
This report summarizes the U.S. Forest Service, Forest Inventory and Analysis (FIA) forest inventory data, collected from 2008 to 2012, for Southern New England, defined as Connecticut, Massachusetts, and Rhode Island. In addition to providing regional and state-level summaries, the reports highlights three focus plots, one average or prototypical plot from each State, as a means to better tell the story of the forests of the region. Forests cover an estimated 5,128,000 acres or 59 percent of Southern New EnglandÑ1,736,000 acres in Connecticut (56 percent of the State), 3,028,000 acres in Massachusetts (61 percent), and 364,000 acres in Rhode Island (55 percent). There was no substantial change in the area of forest land between the current, 2012, and the previous, 2007, FIA inventories.
This report summarizes the second annual inventory of New YorkÕs forests, conducted in 2008-2012. New YorkÕs forests cover 19.0 million acres; 15.9 million acres are classified as timberland and 3.1 million acres as reserved and other forest land. Forest land is dominated by the maple/beech/birch forest-type group that occupies more than half of the forest land. The sound wood volume on timberland has been rising and is currently 37.4 billion cubic feet, enough to produce saw logs equivalent to 93.7 billion board feet.
The first full remeasurement of the annual inventory of the forests of Vermont and New Hampshire was completed in 2012 and covers nearly 9.5 million acres of forest land, with an average volume of nearly 2,300 cubic feet per acre. The data in this report are based on visits to 1,100 plots located across Vermont and 1,091 plots located across New Hampshire. Forest land is dominated by the maple/beech/birch forest-type group, which occupies 60 percent of total forest land area.
Sugar maple (Acer saccharum Marsh.) decline disease, decreased growth, and regeneration failure have been related to a low supply of Ca and Mg. There is increased interest in augmenting cation availability via liming, but there is little information on the amounts of lime required and the longevity of the lime treatment. A single application of 22.4 Mg ha-1 of dolomitic limestone in 1985 at four forested sites in Potter County, PA has shown that soil, soil water, and sugar maple foliage chemistry are significantly altered by liming and the changes in soils and foliage persist as long as 21-yr post-treatment. By 2001, only 3 kg ha-1 of lime remained undissolved while increases in exchangeable Ca and Mg, and pH continued through 2006 at depths up to 35 to 45 cm.