The Natural Distribution of Red Pine in New York

Ecology ◽  
1952 ◽  
Vol 33 (4) ◽  
pp. 500-512 ◽  
Author(s):  
David B. Cook ◽  
Ralph H. Smith ◽  
Earl L. Stone
Ecology ◽  
1980 ◽  
Vol 61 (1) ◽  
pp. 25-29 ◽  
Author(s):  
Peter Tobiessen ◽  
Mary B. Werner

2019 ◽  
Vol 39 (2) ◽  
pp. 226 ◽  
Author(s):  
Erin R. Abadir ◽  
Joseph M. Marschall ◽  
Daniel C. Dey ◽  
Michael C. Stambaugh

1974 ◽  
Vol 4 (3) ◽  
pp. 366-371 ◽  
Author(s):  
Edward P. Farrell ◽  
Albert L. Leaf

A core sampling technique was used for the investigation of root numbers in a 42-year-old red pine (Pinusresinosa Ait.) irrigation – K fertilization experimental area of a K deficient sandy outwash plain in the southeastern Adirondack Mountain Region of New York. Soil cores were collected from plots, 6 years after initiation of treatments, at 0–15 and 15–30 cm depths, using a 5.2 cm diameter corer. Roots were separated from soil cores by a sieving technique. Root tips, including each tip of mycorrhizal structures, were counted by classes established on the basis of morphological characteristics. Numbers of root tips were greater under nonfertilized than fertilized plots, and greater under irrigated than nonirrigated plots. This response pattern did not follow that of wood volume increment, which was greatest in fertilized plots, but was similar to the previously reported pattern in soil microarthropod numbers. The great natural variation observed suggests that root tip numbers may be highly sensitive to changes in soil conditions. Calculated sampling intensity, based on the variance estimates, and specific levels of probabilities (α and β) and allowable sampling error (ε), indicated the need for high numbers of samples.


1974 ◽  
Vol 106 (3) ◽  
pp. 247-251 ◽  
Author(s):  
John J. Piston ◽  
Gerald N. Lanier

AbstractTwo types of field bioassays of the relative attractiveness of various pheromone sources to Ips pini were conducted at Wanakena, N.Y., and at Warrensburg, N.Y. In the first test, the numbers and sex ratios of beetles responding to boring males from New York, Idaho, and their F1 and backcross hybrids graded down in the order of "blood relationship." The intermediate attractiveness of hybrids indicates that hybrids produce pheromones of both parents. In the second test, New York males reared in white pine attracted greater numbers of beetles than those reared in red pine and beetles boring in white pine were more attractive than those boring in red pine.


2003 ◽  
Vol 135 (2) ◽  
pp. 309-311 ◽  
Author(s):  
Peter de Groot ◽  
Therese M. Poland

Hylastes opacus Erichson is a recently introduced bark beetle in North America (Bright and Skidmore 1997; Hoebeke 1994; Rabaglia and Cavey 1994; Wood 1992). It is widely distributed in the Palearctic region, where it usually breeds in stumps and roots of dead or dying pines (Pinus) and occasionally other conifers (Hoebeke 1994). Like many species of bark beetles, H. opacus uses host volatiles as cues to search for suitable host material for feeding and establishment of broods. Hoebeke (1994) reported the attraction of H. opacus to ethanol-baited logs of Scots pine (Pinus sylvestris L.) and red pine (Pinus resinosa Ait.) in New York, United States of America. In Sweden, Schroeder and Lindelöw (1989) observed H. opacus responding to (−)-α-pinene and to ethanol released separately, but a synergistic increase in response did not occur when these two compounds were released together. In later experiments, Lindelöw et al. (1993) found that traps baited with ethanol alone, ethanol + (−)-α-pinene, and spruce turpentine caught significantly more H. opacus than unbaited traps. In these experiments, (−)-α-pinene alone was not attractive, and when (−)-α-pinene was combined with spruce turpentine and ethanol, it reduced catches of H. opacus. In 2002, while investigating attractants for the pine shoot beetle, Tomicus piniperda (L.) (TM Poland, P de Groot, S Burke, D Wakarchuk, RA Haack, and RW Nott, unpublished data), we unexpectedly found significant numbers of H. opacus in one of our experiments. Here we report that H. opacus is strongly attracted to nonanal.


2005 ◽  
Vol 35 (8) ◽  
pp. 1978-1983 ◽  
Author(s):  
C AZ Buxbaum ◽  
C A Nowak ◽  
E H White

Growth of Pinus resinosa Ait. (red pine) on a potassium-deficient sandy soil at the Charles Lathrop Pack Demonstration Forest in Warrensburg, New York, is influenced by fine-textured lenses at 2–3 m below grade. A possible mechanism for an observed increase in surface soil potassium over time is nutrient uptake by red pine roots penetrating into these fine-textured, subsoil layers, and subsequent cycling of these nutrients between foliage and surface soil horizons. To test this hypothesis, we applied nutrient tracers directly to the deep subsoil and measured their uptake over several growing seasons: Strontium was applied in 1989 and 1993, while rubidium-free potassium (the Rb/K reverse tracer method) was applied only in 1993. Trees treated in 1989 had significantly greater concentrations of foliar and bud strontium than control trees, and trees treated only in 1993 also demonstrated significant uptake of potassium 2 years after treatment. These effects were present regardless of whether the trees had been surface-fertilized with potassium five decades earlier. The results demonstrate the importance of subsoil nutrient pools in forest ecosystem function.


1991 ◽  
Vol 55 (3) ◽  
pp. 847-850 ◽  
Author(s):  
C. A. Nowak ◽  
R. B. Downard ◽  
E. H. White
Keyword(s):  
New York ◽  
Red Pine ◽  

2005 ◽  
Vol 81 (4) ◽  
pp. 502-515 ◽  
Author(s):  
Thad E Yorks ◽  
Kenneth B Adams

In January 1998, an ice storm caused severe damage to the rare jack pine – pitch pine barrens in northeastern New York. We quantified tree damage and recovery in seven barrens stands and an adjacent red pine stand. Ice storm damage was variable among stands with 44% to 94% of trees exhibiting damage. Live tree basal area (BA) was reduced by 9% to 45% in six of the eight stands, and dead tree BA increased in all stands. In mixed jack pine – pitch pine stands, the percent of jack pines dead after the ice storm (71% to 91%) was much higher than red maple (0% to 7%) or pitch pine (17% to 25%).Mortality of pitch pine was very low due largely to its ability to produce epicormic growth. Red pine exhibited more severe damage than eastern white pine. Because pine regeneration remains absent or sparse in the barrens stands, deciduous trees and ericaceous shrubs may eventually replace pine species. Mortality due to ice damage may exacerbate this problem in the absence of some regenerating disturbance, such as fire or harvesting. Key words: ice storm damage, pine barrens, Pinus banksiana, jack pine, Pinus rigida, pitch pine, Pinus resinosa, red pine, Pinus strobus, eastern white pine, Acer rubrum, red maple


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