Regeneration of Northern Hardwoods in the Northeast with the Shelterwood Method

1991 ◽  
Vol 8 (3) ◽  
pp. 99-104 ◽  
Author(s):  
Peter R. Hannah
Keyword(s):  
Sugar Maple ◽  
Canopy Cover ◽  
Additional Treatment ◽  
Northern Hardwoods ◽  
Seedling Density ◽  
Yellow Birch ◽  
Northern Hardwood ◽  
White Ash ◽  
Soil Scarification ◽  
Preferred Species

Abstract Study plots (1/4 ac) were located in four northern hardwood stands in Vermont, and shelterwood canopy covers of 40, 60, 80, and 100%, and a control (no cutting) were established. Regeneration on small plots within the treated areas was sampled over a 3-year period and the composition of saplings determined after 6 years. While there were substantial increases in amount of regeneration under most canopy covers, there was no significant differences due to treatment. Some important trends, however, were evident. Sugar maple showed some increase in seedling density under most canopy densities with up to 68,000 new sugar maple seedlings per acre under 60% canopy cover. Yellow birch did best under 40 to 80% canopy cover and with good soil scarification. White ash increased under most densities but was best at about 80% canopy cover. Competitors, beech, striped maple, and hobblebush, increased under most densities. At about 60% canopy cover and less, raspberries and blackberries, pin cherry, and other shade-intolerant species increase in abundance. Among regeneration less than 3 ft all after 3 years, preferred species outnumbered less preferred species by 5 to 1. Among regeneration over 3 ft tall when examined 6 years after treatment, the less preferred species, on average, outnumber preferred species by 2 to 1 (sugar maple 0-3430/ac, yellow birch 0-1920/ac, beech 200-2220/ac and striped maple 0-3130/ac). Most beech regeneration seemed to arise as root suckers. Small striped maple grew rapidly and assumed dominance among the regeneration when released. Northern hardwoods have diverse composition in the overstory, and much of the regeneration tallied after 3 years was already in place when the shelterwood cuts were made. Advanced regeneration as well as new regeneration is the key to success, or failure, if it is predominantly undesirable species. In implementing a shelterwood in northern hardwoods, 60 to 80% canopy cover seems good for most species. All trees below the main canopy should be cut to create a high canopy shade. Undesirable species should be controlled by cutting or possibly herbicides before or when the stand is cut, with additional treatment as necessary to maintain desired composition. North. J. Appl. For. 8(3):99-104.

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 Decaying Logs as Germination Sites in Northern Hardwood Forests

1997 ◽  
Vol 14 (4) ◽  
pp. 178-182 ◽  
Author(s):  
Gregory G. McGee ◽  
John P. Birmingham
Keyword(s):  
New York ◽  
Forest Floor ◽  
Sugar Maple ◽  
Ground Cover ◽  
Tree Regeneration ◽  
Red Spruce ◽  
Yellow Birch ◽  
Northern Hardwood Forests ◽  
Northern Hardwood ◽  
Soil Scarification

Abstract While several authors have noted tree regeneration on decaying logs, the role that "nurse logs" play in maintaining tree diversity in eastern North American forests has remained unquantified. We sampled small seedling (≤ 5 cm high) densities of seven tree species on and directly adjacent to logs in two northern hardwood stands in the Adirondack mountains of New York. Polar ordination of 42 microsite plots revealed distinctly different small seedling communities on logs vs. forest floor. Yellow birch and red spruce densities were 24 times and 5 times greater on logs than forest floor, while those of sugar maple and striped maple were 8 times and 4 times greater on the forest floor. Maintaining a natural level (~5% ground cover) of well distributed logs can supplement site preparation techniques such as soil scarification to provide regeneration sites for yellow birch and red spruce, particularly in heavily stocked northern hardwood stands. North. J. Appl. For. 14(4):178-182.

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.

Effect of site characteristics and 1st- and 2nd-year seedling densities on forest development in a northern hardwood forest

1992 ◽  
Vol 22 (12) ◽  
pp. 1860-1868 ◽  
Author(s):  
Sally W. Thurston ◽  
Marianne E. Krasny ◽  
C. Wayne Martin ◽  
Timothy J. Fahey
Keyword(s):  
Sugar Maple ◽  
Stand Age ◽  
Hubbard Brook Experimental Forest ◽  
Yellow Birch ◽  
Site Factors ◽  
Clear Cut ◽  
White Ash ◽  
Clear Cutting ◽  
Seed Availability ◽  
Soil Scarification

Factors influencing the initial colonization and subsequent (18-year) survivorship of trees were studied in two clear-cut watersheds in the Hubbard Brook Experimental Forest in New Hampshire. Variation in microsite conditions associated with the harvest operations (e.g., soil scarification, slash) and physical gradients within the watershed were particularly important in determining 1st- and 2nd-year densities of pin cherry (Prunuspensylvanica L.) and yellow birch (Betulaalleghaniensis Britt.), whereas factors relating to seed availability and the presence of advance seedlings and sprouts were important in determining 1st- and 2nd-year white ash (Fraxinusamericana L.) density. The 1st- and 2nd-year densities of sugar maple (Acersaccharum Marsh.) and beech (Fagusgrandifolia Ehrh.) were relatively independent of factors measured in this study and were probably related to both seed availability and the presence of advance seedlings and sprouts. Physical site factors immediately following clear-cutting continued to be important in determining the density of pin cherry and yellow birch at stand age 18 years, whereas 2nd-year sugar maple and beech seedling and sprout densities were the most important factors in determining the densities of these species 18 years following clear-cutting.

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.

Identifying roots of northern hardwood species: patterns with diameter and depth

2008 ◽  
Vol 38 (11) ◽  
pp. 2862-2869 ◽  
Author(s):  
Ruth D. Yanai ◽  
Melany C. Fisk ◽  
Timothy J. Fahey ◽  
Natalie L. Cleavitt ◽  
Byung B. Park
Keyword(s):  
Fine Roots ◽  
Sugar Maple ◽  
Rooting Depth ◽  
Betula Alleghaniensis ◽  
Tree Roots ◽  
Mixed Stands ◽  
Northern Hardwood ◽  
White Ash ◽  
Diagnostic Characteristics ◽  
Significant Difference

Forest canopies are often stratified by species; little is known about the depth distribution of tree roots in mixed stands because they are not readily identified by species. We used diagnostic characteristics of wood anatomy and gross morphology to distinguish roots by species and applied these methods to test for differences in the rooting depth of sugar maple ( Acer saccharum Marsh.), American beech ( Fagus grandifolia Ehrh.), and yellow birch ( Betula alleghaniensis Britt.) in two northern hardwood forests. We also distinguished hobblebush ( Viburnum lantanoides Michx.) and white ash ( Fraxinus americana L.) roots. Analysis of plastid DNA fragment lengths confirmed that 90% of the roots were correctly identified. The vertical distribution of fine roots of these species differed by 2–4 cm in the median root depth (P = 0.03). There was a significant difference in the distribution of roots by size class, with fine roots (0–2 mm) being more concentrated near the soil surface than coarser roots (2–5 mm; P = 0.004). The two sites differed by <2 cm in median rooting depths (P = 0.02). The visual identification of roots for the main tree species in the northern hardwood forest allows species-specific questions to be posed for belowground processes.

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 Effects of Scarification Disturbance on the Seedling and Midstory Layer in a Successional Mixed-Oak Forest

2003 ◽  
Vol 20 (2) ◽  
pp. 85-91 ◽  
Author(s):  
John M. Lhotka ◽  
James J. Zaczek
Keyword(s):  
Acer Saccharum ◽  
Sugar Maple ◽  
Growing Season ◽  
Quercus Alba ◽  
Seedling Density ◽  
White Oak ◽  
Treatment Results ◽  
Southern Illinois ◽  
Soil Scarification ◽  
Oak Seedlings

Abstract This study investigated whether soil scarification during the presence of abundant white oak (Quercus alba L.) acorns and other mast could be used to increase the density of oak reproduction and reduce competitive midstory species in a mid-successional mixed-oak upland forest. The study was conducted in a 7.3 ha forest with a mature oak overstory and a well-developed midstory of sugar maple (Acer saccharum Marsh.) and pawpaw (Asmina triloba Dunal.) in southern Illinois. The soil scarification was conducted in the autumn after acorn dissemination using a crawler tractor with a six-tooth brush rake. One growing season after treatment, significantly higher numbers of oak seedlings, primarily white oak, were present in the scarified plots (5,164 ha-1) compared to the control plots (1,273 ha-1). Seedling density of all other species classes did not differ between treatments. Scarification affected 61% of midstory trees and thus reduced their density and competitive position. Of these trees, 21% of stems were completely removed by the scarification treatment. Results suggest that, in the presence of abundant acorns, scarification may increase the number of new oak germinants in stands lacking advanced oak reproduction. Finally, because scarification increased the density of oak seedlings and reduced competing midstory trees, it can play a role in promoting the establishment of advanced oak reproduction. North. J. Appl. For. 20(2):85–91.

Relations entre la microtopographie, les caractéristiques de la couverture morte et la répartition des essences dans une érablière à Bouleau jaune

1988 ◽  
Vol 18 (9) ◽  
pp. 1196-1202 ◽  
Author(s):  
Jean-Claude Ruel ◽  
Denis Loustau ◽  
Marius Pineau
Keyword(s):  
Organic Matter ◽  
Species Distribution ◽  
Forest Floor ◽  
Sugar Maple ◽  
Yellow Birch ◽  
Northern Hardwood ◽  
Rapid Decomposition ◽  
Litter Accumulation ◽  
Weight Losses ◽  
Organic Matter Dynamics

Some effects of microtopography on forest floor, organic matter dynamics, and tree species distribution were studied in a northern hardwood stand near Québec. Forest floor thickness was 12.4 cm in pits while it was only 7.6 cm on mounds. These variations in thickness were attributed to a smaller litter accumulation (186 vs. 318 g m−2 year−1 in pits) and a more rapid decomposition on mounds (weight losses of wooden probes, 17.3 vs. 13.7% in pits). Over 43% of yellow birch stems (Betulaalleghaniensis Britton) were found on mounds in comparison with 20% for beech (Fagusgrandifolia Ehrh.). Sugar maple (Acersaccharum Marsh.) distribution was intermediate between those species. Thus, mounds seem more suitable for yellow birch installation, either because of their characteristics after their formation or because of the thinner forest floor formed on these microsites.

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