scholarly journals Radial growth of hardwoods following the 1998 ice storm in New Hampshire and Maine

2003 ◽  
Vol 33 (2) ◽  
pp. 325-329 ◽  
Author(s):  
Kevin T Smith ◽  
Walter C Shortle
Keyword(s):  
Radial Growth ◽  
Sugar Maple ◽  
Growth Index ◽  
Ice Storm ◽  
Red Maple ◽  
Yellow Birch ◽  
Annual Increment ◽  
White Ash ◽  
Class A ◽  
Mean Annual Increment

Ice storms and resulting injury to tree crowns occur frequently in North America. Reaction of land managers to injury caused by the regional ice storm of January 1998 had the potential to accelerate the harvesting of northern hardwoods due to concern about the future loss of wood production by injured trees. To assess the effect of this storm on radial stem growth, increment cores were collected from northern hardwood trees categorized by crown injury classes. For a total of 347 surviving canopy dominant and subdominant trees, a radial growth index was calculated (mean annual increment for 1998–2000 divided by the mean annual increment for 1995–1997). Sugar maple (Acer saccharum Marsh.), yellow birch (Betula alleghaniensis Britt.), white ash (Fraxinus americana L.), and red maple (Acer rubrum L.) categorized in injury class A (crown loss of less than one-half) had mean growth index values of approximately 1.0, indicating no loss of mean radial growth after 3 years. For injury class B (crown loss of one-half to three-quarters) and class C (crown loss greater than three-quarters), growth index values significantly decreased for sugar maple, yellow birch, and red maple. For white ash, growth index values of classes B and C were not significantly different from those of class A trees. Growth index values of A. saccharum and A. rubrum in injury class C were the lowest of those measured. These results indicated that the severity of growth loss due to crown injury depends on tree species and crown replacement as well as the extent of crown loss.

scholarly journals Glaze Damage in a Young Yellow Birch Stand in Southern Quebec, Canada

2001 ◽  
Vol 18 (1) ◽  
pp. 14-18 ◽  
Author(s):  
Richard Zarnovican
Keyword(s):  
Sugar Maple ◽  
Ice Storm ◽  
Storm Damage ◽  
Linear Modeling ◽  
Yellow Birch ◽  
Precommercial Thinning ◽  
White Ash ◽  
Hardwood Species ◽  
Log Linear ◽  
Ice Storm Damage

Abstract The relationships between three hardwood species, social position of trees, precommercial thinning treatment and ice storm damage were studied in a young hardwood stand in southern Quebec. The association between these variables was determined using log-linear modeling. Severity of the glaze damage was much higher for yellow birch than for sugar maple and white ash. As for the thinning treatment, yellow birch had the highest damage when heavy thinning from below was used. North. J. Appl. For. 18(1):14–18

scholarly journals Long-Term Growth of Crop Trees After Release in Northern Hardwoods

1997 ◽  
Vol 14 (3) ◽  
pp. 147-151 ◽  
Author(s):  
William B. Leak ◽  
Dale S. Solomon
Keyword(s):  
Sugar Maple ◽  
Basal Area ◽  
Response To Treatment ◽  
Red Maple ◽  
Long Term Effects ◽  
Yellow Birch ◽  
White Ash ◽  
Paper Birch ◽  
And Control

Abstract Diameter growth of crop trees of paper birch, sugar maple, yellow birch, white ash, beech, and red maple was remeasured for 31 yr following a heavy release, light release, species removal, and control applied to an evenaged 25 yr old northern hardwood stand in New Hampshire. Under all regimes, final dbh of sampled crop trees was positively related to initial dbh. White ash showed no significant or consistent increase in final dbh in response to treatment, expressed in terms of residual basal area per acre. Paper birch, beech, and red maple had final average diameters up to about 2 in. larger due to heavy release as compared with the control. Sugar maple showed a gain of up to 1 in. in final dbh over the 3l yr period, while yellow birch showed a similar, though nonsignificant, gain. The study shows the long-term effects of release treatments, and the importance of releasing larger trees and responsive species. North J. Appl. For. 14(3):147-151.

Sap yields, sugar content, and soluble carbohydrates of saps and syrups of some Canadian birch and maple species

1987 ◽  
Vol 17 (3) ◽  
pp. 263-266 ◽  
Author(s):  
A. R. C. Jones ◽  
I. Alli
Keyword(s):  
Sap Flow ◽  
Sugar Maple ◽  
Sugar Content ◽  
Soluble Carbohydrates ◽  
Red Maple ◽  
White Birch ◽  
Yellow Birch ◽  
Total Carbohydrate ◽  
Total Carbohydrate Content ◽  
Maple Sap

During the spring of 1984 and 1985, white birch (Betulapapyrifera Marsh), sweet birch (B. lenta L), and yellow birch (B. alleghaniensis Britt.) were tapped to determine sap yields and syrup characteristics. These properties were compared with sap yields and syrup produced from sugar maple (Acersaccharum Marsh) and red maple (A. rubrum L). The sap flow seasons were as follows: white birch, 23 days (April 7–29, 1984) and 29 days (April 5 – May 3, 1985); sweet birch, 26 days (1984); yellow birch, 25 days (1985). The sap flow season for the maple species was much earlier than the birch species. Maple sap flow seasons were as follows: sugar maple, 16 days (March 28 – April 12, 1984) and 45 days (March 10 – April 23, 1985); red maple, 44 days (March 11 – April 23, 1985). Sap yields were as follows: white birch, 80.5 L in 1984 (1.0% sap) 51.0 L in 1985 (1.0% sap); sweet birch, 48.0 L in 1984 (0.5% sap); yellow birch, 28.4 L in 1985 (0.5% sap); red maple, 30.6 L in 1985 (2.3% sap); sugar maple, 53.5 L in 1985 (4.5% sap). Sap analyses showed the average total carbohydrate content of all birch saps and all maple saps was 9.2 and 24.5 g/L, respectively. The average sugar contents of the syrups from the birch saps and the maple saps were 302 and 711 g/L, respectively. The average pH of birch and maple saps were similar but the average pH of the syrups obtained from the birch saps was substantially lower than that of the syrups obtained from the maple saps.

22-Year Growth of Four Planted Hardwoods

1986 ◽  
Vol 3 (2) ◽  
pp. 69-72 ◽  
Author(s):  
Susan Laurane Stout
Keyword(s):  
Sugar Maple ◽  
Black Cherry ◽  
Red Maple ◽  
Old Field ◽  
Forest Landowners ◽  
Northern Hardwood ◽  
White Ash ◽  
Hardwood Species ◽  
Initial Spacing ◽  
Preferred Species

Abstract Planting of northern hardwood species interests forest landowners and managers who wish to continue growing pure or nearly pure stands of high-value species, enhance old-field conversion to preferred species, or reforest areas where natural regeneration has failed. Little data on planted hardwoods can be found, however. This paper reports on 22 years of growth of a northern hardwood plantation established in 1961 containing red maple, black cherry, sugar maple, and white ash. The data show that plantings of these species can succeed on good sites with weed control over the first few years, protection from animal predators, and close initial spacing. North. J. Appl. For. 3:69-72, June 1986.

scholarly journals Improving the Composition of Beech-Dominated Northern Hardwood Understories in Northern Maine

2011 ◽  
Vol 28 (4) ◽  
pp. 186-193 ◽  
Author(s):  
Andrew S. Nelson ◽  
Robert G. Wagner
Keyword(s):  
Sugar Maple ◽  
Low Cost ◽  
Optimal Treatment ◽  
Red Maple ◽  
Yellow Birch ◽  
Northern Hardwood ◽  
Hardwood Species ◽  
Understory Composition ◽  
Glyphosate Herbicide ◽  
Selection Harvesting

Abstract The natural regeneration that develops following the shelterwood and selection harvesting of northern hardwood stands across the Northeast is often plagued by an overabundance of American beech infected with beech bark disease. This regenerating beech typically dominates and interferes with the regeneration of more desired hardwood species (sugar maple, yellow birch, and red maple), lowering the productivity and value of future stands. We tested factorial combinations of glyphosate herbicide (Accord Concentrate) rate and surfactant (Entrée 5735) concentration to identify an optimal treatment that would maximize beech control while minimizing sugar maple injury. Third-year posttreatment results revealed that glyphosate rate was a more important factor than surfactant concentration in reducing beech abundance and preserving sugar maple. The optimal treatment (0.56‐1.12 kg/ha of glyphosate plus 0.25‐0.5% surfactant) selectively removed 60‐80% of beech stems, whereas sugar maple control was less than 20%. The five dominant hardwood species differed substantially in their susceptibility to the treatments in the following decreasing order: beech > striped maple > yellow birch > red maple > sugar maple. Similar results produced using a backpack mistblower suggested transferability of treatment effects to operational applications using a tractor-mounted mistblower. Our findings indicate that this relatively low-cost and effective treatment can substantially improve the understory composition of northern hardwood stands.

scholarly journals Height-Diameter Equations for Select New Hampshire Tree Species

2011 ◽  
Vol 28 (3) ◽  
pp. 157-160 ◽  
Author(s):  
Andrew J. Fast ◽  
Mark J. Ducey
Keyword(s):  
New Hampshire ◽  
Tree Species ◽  
Sugar Maple ◽  
Eastern Hemlock ◽  
Northern Hardwood Forest ◽  
Red Maple ◽  
Northern Hardwood ◽  
White Ash ◽  
Paper Birch ◽  
Bartlett Experimental Forest

Abstract Height-diameter equations are important in modeling forest structure and yield. Twenty-seven height-diameter equations were evaluated for eight tree species occurring in the northern hardwood forest of New Hampshire using permanent plot data from the Bartlett Experimental Forest. Selected models with associated coefficients are presented for American beech, eastern hemlock, paper birch, red maple, red spruce, sugar maple, white ash, yellow birch, and all 16 species combined.

scholarly journals Competition, Climate, and Size Effects on Radial Growth in an Old-Growth Hemlock Forest

Forests ◽  
2019 ◽  
Vol 11 (1) ◽  
pp. 52 ◽  
Author(s):  
Seth W. Bigelow ◽  
James R. Runkle ◽  
Evan M. Oswald
Keyword(s):  
Radial Growth ◽  
Sugar Maple ◽  
Growth Models ◽  
Tree Size ◽  
Eastern Hemlock ◽  
Betula Alleghaniensis ◽  
Climate Trends ◽  
Yellow Birch ◽  
Old Growth ◽  
Climatic Indices

Research Highlights: We applied neighborhood and dendro-ecological methods in a stand with a 33-year record of forest dynamics, finding that growth will decrease for several species under predicted climate trends. Background and Objectives: Conventional tree-ring analysis removes the influence of competition and size on growth, precluding assessment of the relative influence of these factors. An old-growth eastern hemlock forest in east–central New York was mapped in 1978 and was measured at eight-year intervals since then. Our objective was to use these data to examine the influence of climate, neighborhood, and tree size on radial growth. Materials and Methods: We evaluated an array of climatic indices to find which ones had the strongest influence on radial growth from increment cores of eastern hemlock (Tsuga canadensis L.), yellow birch (Betula alleghaniensis Britton), and sugar maple (Acer saccharum Marsh.). We used the strongest climatic indices in combination with neighborhood and target-tree size information to create growth models for the three tree species. Results: Size accounted for 2% to 21% of observed growth; the shade-tolerant sugar maple and eastern hemlock grew fastest when large, but the mid-tolerant yellow birch grew fastest when small. Competition accounted for 9% to 21% of growth; conifers had a weaker competitive effect than deciduous trees, and eastern hemlock was less sensitive to competition than sugar maple and yellow birch. Climate accounted for only 2% of growth variation; eastern hemlock showed a positive response to warming climate trends, but yellow birch and sugar maple showed negative responses. Conclusions: Predicted climate trends are likely to result in decreased growth of sugar maple and yellow birch, and the sensitivity of these species to competition suggests the effect will be exacerbated when they grow in crowded conditions.

scholarly journals Height Development of Upper-Canopy Trees Within Even-Aged Adirondack Northern Hardwood Stands

2004 ◽  
Vol 21 (3) ◽  
pp. 117-122 ◽  
Author(s):  
Ralph D. Nyland ◽  
David G. Ray ◽  
Ruth D. Yanai
Keyword(s):  
Sugar Maple ◽  
Height Growth ◽  
Fagus Grandifolia ◽  
Growth Patterns ◽  
Betula Alleghaniensis ◽  
Yellow Birch ◽  
Northern Hardwood ◽  
White Ash ◽  
Advance Regeneration ◽  
Canopy Trees

Abstract Knowledge of the relative rates of height growth among species is necessary for predicting developmental patterns in even-aged northern hardwood stands. To quantify these relationships, we used stem analysis to reconstruct early height growth patterns of dominant and codominant sugar maple (Acer saccharum Marsh.), yellow birch (Betula alleghaniensis Britton), white ash (Fraxinus americana L.), and America beech (Fagus grandifolia Ehrh.) trees. We used three stands (aged 19, 24, and 29 years) established by shelterwood method cutting preceded by an understory herbicide treatment. We analyzed 10 trees of each species per stand. Height growth was similar across stands, allowing us to develop a single equation for each species. Our data show that yellow birch had the most rapid height growth up to approximately age 10. Both sugar maple and white ash grew more rapidly than yellow birch beyond that point. Beech consistently grew the slowest. White ash had a linear rate of height growth over the 29-year period, while the other species declined in their growth rates. By age 29, the heights of main canopy trees ranged from 38 ft for beech to 51 ft for white ash. Both yellow birch and sugar maple averaged 46 ft tall at that time. By age 29, the base of the live crown had reached 17, 20, 21, and 26 ft for beech, sugar maple, yellow birch, and white ash, respectively. Live–crown ratios of upper-canopy trees did not differ appreciably among species and remained at approximately 40% for the ages evaluated. These results suggest that eliminating advance regeneration changes the outcome of competition to favor species other than beech. North. J. Appl. For. 21(3):117–122.

Clearcutting Central New York Northern Hardwood Stands

1989 ◽  
Vol 6 (2) ◽  
pp. 75-78 ◽  
Author(s):  
Russell S. Walters ◽  
Ralph D. Nyland
Keyword(s):  
New York ◽  
Sugar Maple ◽  
Site Occupancy ◽  
Black Cherry ◽  
Red Maple ◽  
American Beech ◽  
White Ash ◽  
Central New York ◽  
Commercial Species ◽  
Uniform Cover

Abstract Clearcutting proved effective for regenerating central New York stands that were dominated by sugar maple along with American beech, black cherry, white ash, red maple, and basswood. Findings from five stands for periods of 7-13 years following clearcutting show densities equivalent to 2,400 to 9,400 saplings of commercial species per acre on 64-100% of the milacres sampled. In each stand, a minimum of 81% of the 6.6 ft radius sample plots were stocked with at least one sapling of a commercial species, suggesting that site occupancy will be fairly complete and uniform as these stands mature. All sites contained abundant regeneration of commercial species immediately after logging, ranging from 15,000 to 57,000 seedlings per acre, but as many as 90% of these were less than 1 ft tall. The species composition generally reflected the original forest with abundant sugar maple and American beech. However, large amounts of black cherry and white ash also appeared on some sites. Many bramble seedlings germinated during the first growing season after logging and developed into a dense uniform cover by the third year. However, the brambles declined as crown closure occurred in the new stands, and disappeared before the tenth year. Clearcutting should successfully regenerate stands of New York northern hardwoods having conditions similar to those of this study. North. J. Appl. For. 6:75-78, June 1989.

Seed Storage and Germination Under Northern Hardwood Forests

1975 ◽  
Vol 5 (3) ◽  
pp. 478-484 ◽  
Author(s):  
David A. Marquis
Keyword(s):  
Forest Floor ◽  
Sugar Maple ◽  
Seed Storage ◽  
Red Maple ◽  
Yellow Poplar ◽  
Organic Layers ◽  
Northern Hardwood ◽  
White Ash ◽  
Sowing Seed ◽  
And Storage

The species, quantities, and germination of tree seed stored in the forest floor beneath five northern hardwood stands in Pennsylvania were determined by counting seed found in blocks of forest floor material and running germination tests on them, by burying seed in soil organic layers and observing germination and storage, and by sowing seed on natural seedbeds and observing germination over several years. Quantities of seed in excess of 1 million per acre (2.5 million per hectare) were found to be common, the number of seed of a particular species depending on the number of seed-bearing trees of that species in the overstory and on the length of time seed of that species will remain viable in the forest floor. Sugar maple, eastern hemlock, and American beech normally germinate the year after seed dispersal and do not remain viable in the forest floor. Black cherry, white ash, yellow poplar, red maple, and birch normally germinate over a period of several years after dispersal; and storage in the forest floor for 2 to 5 years is common. Pin cherry seed remain viable in the forest floor for long periods, and large quantities of seed may still be present 30 years or more after pin cherry trees have died out of the overstory.

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