Vermont's forests are valuable ecologically, economically, and socially. Covering nearly 80 percent of the state, forests provide jobs, stability to the landscape, wildlife habitats, biological diversity, clear water, scenic vistas, and diverse recreational opportunities. While changes are always occurring to the forests, there are values that Vermonters want to maintain.
A Forest Resource Plan was developed to sustain the many values and meet the various demands on the forest resource. The vision states that: In the future, the forests of Vermont will consist of healthy and sustainable ecosystems, with a prosperous and sustainable forest products industry, abundant recreational opportunities, and a combination of ownership patterns supporting a working forest landscape and undeveloped forest land.
The January 1998 ice storm impacted 951,589 acres, one-fifth of the forest land in Vermont (See map). The heavy ice loads that weighted trees and caused serious branch and stem breakage affected low elevations in the Champlain Valley (up to 1000 feet) and higher elevations in central and eastern Vermont. Sugar maples were most commonly injured, but damage was more serious on beech and birch trees. Sugarmakers affected by the storm are estimated to have reduced the number of taps by 75,000. Individual tree recovery or decline is expected to occur over the next 3 to 5 years. Several monitoring projects are underway to assess the long-term impact of the storm to the State's forest resource.
On a statewide basis, trends in sugar maple condition varied little from previous years, with 93% of sugar maples in the North American Maple Project in a healthy condition, with less than 15 percent crown dieback. The only tree health indicator that showed significant change was mortality as a result of the ice storm. Average annual mortality of overstory trees from 1989 to 1997 was between 0.1 and 0.9%, but rose to 1.7 % in 1998, due to heavy ice damage.
The summer of 1998 was the second wettest and the fifth warmest, as opposed to the drought conditions that occurred during the summer of 1999. In 1998, the warm humid air created conditions that favored development of leaf diseases, especially on hardwoods. Anthracnose, a disease which causes dead patches on leaves, was recorded on 243,730 acres of forest. Damage was heaviest on sugar maple, paper birch, and yellow birch. While this foliage disease can reduce the vigor of affected trees, most are expected to recover.
Birch defoliation by birch leaf miners and anthracnose was observed on 21,283 acres of forest in 1998, an increase from 3,842 acres in 1997. Tree recovery is expected, except in locations where defoliation has occurred several years in succession, causing reduced tree vigor, or in areas where trees were already stressed from ice storm injury.
| Pear thrips, a recent pest on sugar maple, defoliated
36,081 acres of forest in 1998. Damage was especially severe in the southern
part of the state. In some stands, defoliation was combined with anthracnose
disease and trees were left with small ineffective leaves throughout the
growing season. High populations of the maple trumpet skeletonizer also
combined with leaf diseases and left some woods looking brown, with dead and
Hardwood decline and dieback, prevalent in 1997, decreased to 5,675 acres in 1998. Spruce mortality was reduced to 784 acres, mostly at high elevations. Tree recovery may have been related to abundant precipitation which occurred in 1998. Historically, wet years have been associated with lower acreages of declining trees.
An unusual white pine malady was observed in scattered locations throughout the state in 1998, especially in southeastern Vermont. No single causal agent was consistently associated with the unthrifty crowns. Also, many species had heavy seed crops. Spruce, fir, pine, red maple, oak and beech are some of the species observed with heavy seed production, which impacts crown appearance and affects tree health.
Christmas Tree Problems
Two insect pests that cause serious damage in Christmas tree plantations were found at higher than normal levels in 1998. Balsam shootboring sawfly populations increased dramatically, affecting about 260 acres. This insect attacks the buds as shoots are emerging and can cause mortality of the new shoots. The balsam gall midge causes deformities to new shoots. Galls were found in nearly every balsam fir Christmas tree plantation visited in northern Vermont.
Two regionally significant exotic insects , the hemlock woolly adelgid and the Asian longhorned beetle, are not currently found in Vermont. The hemlock woolly adelgid is attacking and in some cases causing serious decline of hemlock as near as northern Massachusetts. An external quarantine is in effect to reduce the chances of introduction of the adelgid from infested areas into Vermont. Attempts are underway to eradicate the Asian longhorned beetle from parts of Long Island, New York City, and Chicago, Illinois. This large wood boring insect often prefers maples to other tree species. An action plan is under development by State organizations to provide for a quick response if the insect is found in Vermont. The Department of Forests, Parks and Recreation is cooperating with the University of Vermont on a State and regional public awareness program concerning the beetle.
Air quality and Forests
Ground level ozone injury to forests is being monitored annually at specific sites statewide as part of the National Forest Health Monitoring program. While ozone exposure can reduce tree growth and tree resiliency, low level leaf damage has been detected on monitored sites in Vermont. Sensitive plant species at 60% of the locations surveyed in 1998 had symptoms of ozone injury.
The New England Governors and Eastern Canadian Premieres have given priority to addressing acid deposition impacts on forests through the implementation of their Acid Rain Action Plan of 1998. The action plan identifies mapping forest sensitivity to acid deposition as one of its priorities. Forest resilience to acid deposition depends largely on the ability of soils to buffer the acid inputs, thereby keeping soil nutrition stable for tree growth. The mapping project in Vermont will be completed in 2001.
Interest in regional forest condition prompted the implementation of the National Forest Health Monitoring Program and the North American Maple Project.
National Forest Health Monitoring ProgramThe objective is to assess trend in tree condition and forest stressors. All of the New England States have been involved since the program was initiated in 1990. Results indicate that there has been minimal change in crown condition in the last 5 years. In 1994, 99 percent of trees greater than 5 inches diameter had normal crown fullness. About 96 percent of the trees had little or no crown dieback, and 78 percent showed no measurable signs of damage. The most common damage was decay indicators, which were more evident on hardwoods than softwoods. Additional surveys indicate there are concerns for individual species such as ash, butternut and hemlock due to various damage agents.
|Updated: November 1999|
|1998 Forest Health Highlights - Vermont|
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