Exploring the Recruitment Dynamics of Sugar Maple and Yellow Birch Saplings into Merchantable Stems Following Harvesting in the Acadian Forest Region of New Brunswick, Canada

2021 ◽  
Author(s):  
Alex Noel ◽  
Jules Comeau ◽  
Salah-Eddine El Adlouni ◽  
Gaetan Pelletier ◽  
Marie-Andrée Giroux
Keyword(s):  
New Brunswick ◽  
Sugar Maple ◽  
Basal Area ◽  
Stem Density ◽  
Yellow Birch ◽  
Probability Of Occurrence ◽  
Silvicultural Treatment ◽  
Forest Region ◽  
Wide Range ◽  
Acadian Forest

The recruitment of saplings in forest stands into merchantable stems is a very complex process, thus making it challenging to understand and predict. The recruitment dynamics in the Acadian Forest Region of New Brunswick are not well known or documented. Our objective was to draw an inference from existing large scale routine forest inventories as to the different dynamics behind the recruitment from the sapling layer into the commercial tree size layer in terms of density and occurrence of sugar maple (Acer saccharum Marsh.) and yellow birch (Betula alleghaniensis Britt.) following harvesting, by looking at many factors on a wide range of spatial and temporal scales using models. Results suggest that the variation in density and probability of occurrence is best explained by the intensity of silvicultural treatment, by the merchantable stem density in each plot, and by the proportion of merchantable basal area of each group of species. The number of recruits of sugar maple and yellow birch stems tend be higher when time since last treatment increases, when mid to low levels of silvicultural treatment intensity were implemented, and within plots having intermediate levels of merchantable stem density. Lastly, our modeling efforts suggest that the probability of occurrence and density of recruitment of both species tend to increase while its share of merchantable basal area increases.

The Acadian forest: Historical condition and human impacts

2003 ◽  
Vol 79 (3) ◽  
pp. 462-474 ◽  
Author(s):  
J. Loo ◽  
N. Ives
Keyword(s):  
Boreal Forest ◽  
Sugar Maple ◽  
Red Spruce ◽  
Balsam Fir ◽  
Forest Types ◽  
The South ◽  
Yellow Birch ◽  
Maritime Provinces ◽  
Forest Region ◽  
Acadian Forest

The Acadian Forest Region comprises the three Maritime Provinces of Canada, each of which has a distinct history resulting in different patterns of land ownership, land use, and impacts on the forest. The region encompasses a high degree of physiographic and biological diversity, being situated where the warm, moist influence of the Gulf Stream from the south collides with the cold Labrador Current and the boreal forest gradually gives way to mostly deciduous forest. Natural forest types in the Acadian Forest Region include rich tolerant hardwood, similar to the deciduous forests to the south; spruce-fir forest, similar to boreal forest to the north; and an array of coniferous, deciduous, and mixed intermediate types. Red spruce (Picea rubens Sarg.), yellow birch (Betula alleghaniensis Britt.), sugar maple (Acer saccharum Marsh.) and balsam fir (Abies balsamea (L.) Mill.) are considered characteristic of the Acadian Forest Region. Except for one quantitative study in one county of New Brunswick, and another study on Prince Edward Island, most knowledge of the historical forest condition has been gleaned from early descriptions by explorers, surveyors, and settlers of the Maritimes region. Although some regions have been affected much more than others, little, if any forested area has escaped human influence over the past four centuries. A general result of human activities has been a shift in successional status and age distribution, with increased frequency of relatively young, often even-aged, early successional forest types including balsam fir, white spruce (Picea glauca (Moench) Voss), red maple (Acer rubrum L.), white birch (Betula papyrifera Marsh.), and trembling aspen (Populus tremuloides Michx.). Both the abundance and age of late-successional species such as sugar maple, red spruce, eastern hemlock (Tsuga canadensis L. Carrière), yellow birch, cedar (Thuja occidentalis L.), and beech (Fagus grandifolia Ehrh.) have declined. Key words: pre-European forest, Maritime Provinces, historical ecology, witness trees, Acadian forest types, natural disturbance

scholarly journals Tolerant hardwood natural regeneration 15 years after various silvicultural treatments on an industrial freehold of northwestern New Brunswick

2013 ◽  
Vol 89 (04) ◽  
pp. 512-524 ◽  
Author(s):  
Martin Béland ◽  
Bruno Chicoine
Keyword(s):  
New Brunswick ◽  
Natural Regeneration ◽  
Sugar Maple ◽  
Mineral Soil ◽  
Soil Disturbance ◽  
Betula Alleghaniensis ◽  
Yellow Birch ◽  
American Beech ◽  
Partial Cutting ◽  
Selection Cutting

We examined applicability of various partial cutting systems in order to regenerate tolerant hardwood stands dominated by sugar maple (Acer saccarhum), American beech (Fagus grandifolia) and yellow birch (Betula alleghaniensis) on northern New Brunswick J.D. Irving Ltd. freehold land. Sampling of 1065 one-m2 plots in 31 stands managed by selection cutting, shelterwood method and strip or patch cutting and in six control stands allowed a 15-year retrospective study of natural regeneration in stands of low residual densities and with minimal soil disturbance and no control of competing vegetation. Beech regeneration was most abundant in the patch cuts, yellow birch in shelterwood stands and sugar maple in the selection system areas. Results suggest that initial stand conditions influence the composition of the regeneration more than the prescribed treatment. At the stand scale (a few hectares), sugar maple recruitment was positively influenced by its proportion in the initial stand, and negatively by the cover of herbs and shrubs. Yellow birch regeneration was mainly affected by shrub competition. At the plot (1 m2) scale, mineral soil and decayed wood substrates and ground-level transmitted light were determinant factors for yellow birch regeneration. Beech-dominated stands were likely to regenerate to beech. A dense beech sucker understory was promoted in harvested patches. Areas with dense understory of American beech, shrubs, or herbs require site preparation to reduce interference either before or at the time of partial cutting. Shelterwood seed cutting and selection cutting should leave a residual of 12 m2/ha and 17 m2/ha respectively in seed trees uniformly distributed.

scholarly journals Status of soil acidification in North America

2006 ◽  
Vol 52 (Special Issue) ◽  
pp. S3-S13 ◽  
Author(s):  
M.E. Fenn ◽  
T.G. Huntington ◽  
S.B. McLaughlin ◽  
C. Eagar ◽  
A. Gomez ◽  
...  
Keyword(s):  
North America ◽  
Forest Soils ◽  
Soil Acidification ◽  
Sugar Maple ◽  
Base Cations ◽  
Basal Area ◽  
Base Cation ◽  
Eastern United States ◽  
San Bernardino Mountains ◽  
Wide Range

Forest soil acidification and depletion of nutrient cations have been reported for several forested regions in North America, predominantly in the eastern United States, including the northeast and in the central Appalachians, but also in parts of southeastern Canada and the southern U.S. Continuing regional inputs of nitrogen and sulfur are of concern because of leaching of base cations, increased availability of soil Al, and the accumulation and ultimate transmission of acidity from forest soils to streams. Losses of calcium from forest soils and forested watersheds have now been documented as a sensitive early indicator and a functionally significant response to acid deposition for a wide range of forest soils in North America. For red spruce, a clear link has been established between acidic deposition, alterations in calcium and aluminum supplies and increased sensitivity to winter injury. Cation depletion appears to contribute to sugar maple decline on some soils, specifically the high mortality rates observed in northern Pennsylvania over the last decade. While responses to liming have not been systematically examined in North America, in a study in Pennsylvania, restoring basic cations through liming increased basal area growth of sugar maple and levels of calcium and magnesium in soil and foliage. In the San Bernardino Mountains in southern California near the west coast, the pH of the A horizon has declined by at least 2 pH units (to pH 4.0–4.3) over the past 30 years, with no detrimental effects on bole growth; presumably, because of the Mediterranean climate, base cation pools are still high and not limiting for plant growth.

Fate of Spinosad in Litter and Soils of a Mixed Conifer Stand in the Acadian Forest Region of New Brunswick

2002 ◽  
Vol 50 (4) ◽  
pp. 790-795 ◽  
Author(s):  
Dean G. Thompson ◽  
Brenda J. Harris ◽  
Leonard J. Lanteigne ◽  
Teresa M. Buscarini ◽  
Derek T. Chartrand
Keyword(s):  
New Brunswick ◽  
Mixed Conifer ◽  
Forest Region ◽  
Acadian Forest

scholarly journals Modeling tolerant hardwood sapling density and occurrence probability in the Acadian forests of New Brunswick, Canada: Results 14 years after harvesting

2021 ◽  
Vol 97 (02) ◽  
pp. 204-218
Author(s):  
Mohammed Henneb ◽  
Gaetan Pelletier ◽  
Mathieu Fortin ◽  
Nelson Thiffault ◽  
Marie-Andrée Giroux
Keyword(s):  
New Brunswick ◽  
Acer Saccharum ◽  
Sugar Maple ◽  
Basal Area ◽  
Fagus Grandifolia ◽  
Eastern Canada ◽  
American Beech ◽  
Permanent Sample Plots ◽  
Hardwood Species ◽  
Sapling Density

Natural forest regeneration after natural or anthropogenic disturbance is difficult to predict given its high variability. The process is poorly documented for commercial northern hardwood species in the Acadian forest of eastern Canada. Our objective was to identify the silvicultural, environmental, and ecological factors that best explain the variability in sapling density and occurrence of two commercial tolerant hardwood species in New Brunswick: American beech (Fagus grandifolia Ehrh.) and sugar maple (Acer saccharum Marsh.). Forty-three permanent sample plots were established in 2002 and measured before harvesting in 2004. Sapling density and occurrence were measured 14 years after harvesting. The results showed that the interactions between the species and the residual merchantable basal area and between the species and the percent of hardwoods in the original stand best explained the sapling density and occurrence variation of tolerant hardwoods. The sapling density of sugar maple increased with increasing merchantable residual basal area. However, the effect of this variable was not significant for the density of American beech saplings. The density and occurrence of tolerant hardwood saplings both increased along with the percent of hardwoods in the original stand. These results provide an improved understanding about tolerant hardwood regeneration dynamics in New Brunswick forests.

Tree growth, foliar chemistry, and nitrogen cycling across a nitrogen deposition gradient in southern Appalachian deciduous forests

2005 ◽  
Vol 35 (8) ◽  
pp. 1901-1913 ◽  
Author(s):  
Johnny L Boggs ◽  
Steven G McNulty ◽  
Michael J Gavazzi ◽  
Jennifer Moore Myers
Keyword(s):  
Sugar Maple ◽  
Basal Area ◽  
N Deposition ◽  
Deciduous Forests ◽  
Foliar Chemistry ◽  
Yellow Birch ◽  
Foliar N ◽  
Southern Appalachian ◽  
Deposition Gradient ◽  
Response Variables

The declining health of high-elevation red spruce (Picea rubens Sarg.) and Fraser fir (Abies fraseri (Pursh) Poir.) in the southern Appalachian region has long been linked to nitrogen (N) deposition. Recently, N deposition has also been proposed as a source of negative health impacts in lower elevation deciduous forests. In 1998 we established 46 plots on six sites in North Carolina and Virginia dominated by American beech (Fagus grandifolia Ehrh.), sugar maple (Acer saccharum Marsh.), and yellow birch (Betula alleghaniensis Britt). We evaluated several response variables across an N deposition gradient, including annual basal area growth; foliage percent N, Al, P, K, Mg, and Ca; and forest floor percent N, Mg, and C, pH, and potential net nitrification and N mineralization rates. We found a significant linear relationship between N deposition and basal area growth in sugar maple, but not in American beech or yellow birch. In addition, we found a significant relationship between N deposition and foliar chemistry (foliar %N in all species, foliar Mg/N and %K in sugar maple, and %P in sugar maple and yellow birch). Foliar %N of the three studied species was high relative to values reported in other studies in the United States and Canada. Several forest floor response variables (%N, C/N, pH, Mg/N, and potential net nitrification and N mineralization rates and nitrification/mineralization fractions) were also correlated with N deposition. The correlations between the above response variables and N deposition are consistent with the influence of chronic N deposition on forested ecosystems measured in other regions and suggest that chronic N deposition may be influencing forest structure and chemistry within the southern region.

Modeling annualized occurrence, frequency, and composition of ingrowth using mixed-effects zero-inflated models and permanent plots in the Acadian Forest Region of North America

2011 ◽  
Vol 41 (10) ◽  
pp. 2077-2089 ◽  
Author(s):  
Rongxia Li ◽  
Aaron R. Weiskittel ◽  
John A. Kershaw
Keyword(s):  
North America ◽  
Random Effects ◽  
Negative Binomial ◽  
Basal Area ◽  
Forest Growth ◽  
Occurrence Frequency ◽  
Growth And Yield ◽  
Permanent Plots ◽  
Forest Region ◽  
Acadian Forest

Forest tree ingrowth is a highly variable and largely stochastic process. Consequently, predicting occurrence, frequency, and composition of ingrowth is a challenging task but of great importance in long-term forest growth and yield model projections. However, ingrowth data often require different statistical techniques other than traditional Gaussian regression, because these data are often bounded, skewed, and non-normal and commonly contain a large fraction of zeros. This study presents a set of regression models based on discrete Poisson and negative binomial probability distributions for ingrowth data collected from permanent sample plots in the Acadian Forest Region of North America. Models considered here include regular Poisson, zero-inflated Poisson (ZIP), zero-altered Poisson (ZAP; hurdle Poisson), regular negative binomial (NB), zero-inflated negative binomial (ZINB), and zero-altered negative binomial (ZANB; hurdle NB). Plot-level random effects were incorporated into each of these models. The ZINB model with random effects was found to provide the best fit statistics for modeling annualized occurrence and frequency of ingrowth. The key explanatory variables were stand basal area per hectare, percentage of hardwood basal area, number of trees per hectare, a measure of site quality, and the minimum measured diameter at breast height of each plot. A similar model was developed to predict species composition. All models showed logical behavior despite the high variability observed in the original data.

Résultats après 5 ans d'un essai de coupe de jardinage dans une érablière

1992 ◽  
Vol 22 (11) ◽  
pp. 1623-1629 ◽  
Author(s):  
Zoran Majcen ◽  
Yvon Richard
Keyword(s):  
Sugar Maple ◽  
Basal Area ◽  
Yellow Birch ◽  
Area Selection ◽  
Selection Cutting ◽  
Rate Of Growth ◽  
Experimental Area ◽  
Area Growth ◽  
Tree Injuries ◽  
Gross Rate

To study the effects of selection cutting and to determine the optimal residual basal area after such cuttings, an experimental area was established in Sainte-Véronique (Quebec) in 1983. Five-year results indicate that the gross rate of growth increases when residual basal area decreases. The best net annual basal area growth lies between 0.40 and 0.43 m2/ha in selection plots; this is almost twice the growth of control plots. Sugar maple regeneration is excellent no matter the residual basal area. Selection cuttings also resulted in a good yellow birch regeneration, and survival is better, after 5 years, in high residual basal area plots. Yellow birch regeneration is almost absent in control plots. When all factors (growth in basal area, regeneration, and tree injuries) are considered, block 2, with a residual basal area of 19.3 m2/ha, gives the best results after 5 years.

Accroissement d'une érablière à la suite de coupes d'éclaircie: résultats de 20 ans

1996 ◽  
Vol 26 (4) ◽  
pp. 543-549 ◽  
Author(s):  
David Pothier
Keyword(s):  
Sugar Maple ◽  
Basal Area ◽  
Diameter Growth ◽  
Yellow Birch ◽  
Thinning Intensity ◽  
Sugar Maples ◽  
Significant Difference

Two intensities of thinning were executed in a 50-year-old sugar maple stand of the Station forestière de Duchesnay (46°57′N, 71°39′W). Initial basal area was reduced by 22 and 35% in moderate and heavy thinned plots, respectively. Twenty years after treatment, basal area of thinned plots approached that of controls and their basal area in sugar maple (Acersaccharum Marsh.) was larger than that of controls. Diameter growth of sugar maples was proportional to the intensity of thinning and a significant difference was detected between thinned and unthinned plots. Net increment of the 70 sampled plots was proportional to the intensity of thinning but mortality was inversely related to the thinning level. Ingrowth was also proportional to the intensity of thinning but its impact on net increment was relatively low. Ten years following treatment, the number of saplings of yellow birch (Betulaalleghaniensis Britt.) increased with increasing thinning intensity. However, the number of sugar maple saplings remains stable among treatments for all measurement periods. Diameter growth was not affected in sugar maples with annual tapping in comparison to sugar maples with no tapping during the whole study period.

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