Patterns of damage and mortality in red pine plantations following a major ice storm

2005 ◽  
Vol 35 (2) ◽  
pp. 487-493 ◽  
Author(s):  
K L Ryall ◽  
S M Smith

The impact of a major ice storm in eastern Ontario on 28 pine plantations (red pine, Pinus resinosa Ait.; Scots pine, Pinus sylvestris L.; white pine, Pinus strobus L.; and jack pine, Pinus banksiana Lamb.) was examined for 4 years after the event. Degree of crown loss and tree mortality were quantified in relation to tree and stand characteristics (e.g., tree species, diameter at breast height (DBH), stand density, stand edge versus interior). We also tested whether salvaging damaged material reduced subsequent tree mortality. Jack and Scots pine were 2.5 times more likely to be damaged by the ice storm than were red pine and white pine. Overstocked stands, and stands with lower mean DBH, were most susceptible to storm damage. Trees were five times more likely to be damaged in the interior versus the edge of a stand, in contrast with previous findings in hardwood stands. In unsalvaged stands, ca. 75% tree mortality was observed in severely damaged trees (>50% crown loss) compared with ca. 45% tree mortality in salvaged stands. Properly timed thinnings to increase diameter growth and the removal of dead and dying wood from heavily damaged stands are recommended to reduce the long-term effects of ice storms.

1961 ◽  
Vol 37 (1) ◽  
pp. 16-21 ◽  
Author(s):  
J. H. Cayford ◽  
R. A. Haig

In November 1958, an ice storm caused severe bending of stems in young red and Scots pine plantations on the Sandilands Forest Reserve in southeastern Manitoba. A study was carried out to investigate the recovery of bent trees and to determine the extent of permanent damage in the plantations.Between 50 and 100 per cent of the trees in young red pine plantations were bent so severely that their tops were touching the ground. Scots pine plantations were less severely affected. However, both species showed considerable recovery and little or no permanent damage has occurred in plantations younger than 14 or older than 25 years of age. Approximately one quarter of the trees growing in two dense red pine plantations, 16 and 22 years of age, were judged to have been permanently damaged.


2004 ◽  
Vol 34 (12) ◽  
pp. 2528-2540 ◽  
Author(s):  
Ryan E Morgan ◽  
Peter de Groot ◽  
Sandy M Smith

The pine shoot beetle, Tomicus piniperda (L.) (Coleoptera: Scolytidae), was first discovered in North America in 1992, and by the late 1990s it was associated with tree mortality and stand decline throughout southern Ontario. To assess whether this beetle was capable of killing vigorous trees (a primary pest) or would kill only trees already stressed (a secondary pest), we surveyed 43 sites of varying Scots pine (Pinus sylvestris L.), red pine (Pinus resinosa Ait.), and jack pine (Pinus banksiana Lamb.) composition. Specifically, our objective was to determine the relationship between tree and site characteristics and the number of stem and shoot attacks by T. piniperda in southern Ontario. An abundance of recently dead and low-vigour pine trees increased susceptibility of sites to stem and shoot attacks by T. piniperda. Significant negative linear relationships were detected between the number of beetle attacks and the mean height, age, diameter at breast height, basal area, canopy cover, duff depth, and radial growth increments. Pure red pine sites had significantly fewer attacks than sites of pure Scots pine and mixed jack pine, which was attributed to differences in tree vigour and forest management. Tomicus piniperda appears to be a secondary bark beetle in southern Ontario, successfully colonizing only recently dead pine trees or trees suffering from stress.


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


2003 ◽  
Vol 79 (1) ◽  
pp. 47-53 ◽  
Author(s):  
Anthony Hopkin ◽  
Tim Williams ◽  
Robert Sajan ◽  
John Pedlar ◽  
Cathy Nielsen

Following the 1998 ice storm, tree mortality and crown damage were monitored on permanent plots across eastern Ontario from 1998 until 2001. Conifer species were less damaged than hardwoods. Hardwood tree species showing the greatest crown damage included aspen, (Populus tremuloides), basswood (Tilia americana), and white birch (Betula papyrifera); major species showing the least damage included sugar maple (Acer saccharum), red oak (Quercus rubra) and hickory (Carya spp.). Generally, smaller diameter trees showed less damage than larger diameter trees. Significant mortality was recorded to silver maple (Acer saccharinum), basswood, ash (Fraxinus spp.) and aspen in 1998, although mortality in 2000 and 2001 was about 1–2%. Trees sustaining > 75% crown damage usually died by 2001. Key words: ice storm, ice damage, forest health


1956 ◽  
Vol 34 (4) ◽  
pp. 473-500 ◽  
Author(s):  
J. E. Potzger ◽  
Albert Courtemanche

The study includes 19 bogs between 45° 07′ N. and 51° 59′ N. (Fig. 1), spaced at about 50 mile intervals from the St. Lawrence valley across the Laurentian Shield to James Bay (Jack River). Plane service made possible selection of excellent bogs for boring in wilderness regions. The plane landed on lakes near the bogs selected. Up to lat. 47° N. five major climatic changes are recognized for Quebec and are referred to as Q-1 to Q-5. The pollen profiles suggest that an initial, pronounced warm period (Q-1) (correlative with the Lake Timiskaming retreat) followed by cooling (Q-2), very likely also accompanied by local glaciation (correlative with the Cochrane halt), prevailed from the St. Lawrence valley to Lac Soscumica bog (50° 39′ N.). The initial warm period is marked by prominent pine peaks accompanied by an impressive minor oak peak. During the major xerothermic period (Q-3), all bogs record a very long and prominent pine climax, with replacement of Pinus banksiana by the white–red pine group up to the Lacroix River bog (49° 02′ N). From Clova (48° 07′ N.) to Jack River bog (51° 59′ N.) jack pine replaced red white pine, while the upper half of the profile accumulated. This shows jack pine with a striking bimodal pattern of representation. Also, north of Clova, jack pine formed an important association with Picea mariana during the more recent past, introducing the forest type which prevails up there today. From the St. Lawrence valley (45° 07′ N.) to the lower edge of the Shield at Saint-Lin (45° 55′ N.) white–red pine held an important place in the forest cover up to the present (represented by the close of the bog mat). The single most striking feature of the study is that red–white pine penetrated as important forest associates to the Rupert River (51° 28′ N.). No doubt white–red pine extended their range northward during the prominent warm–dry period (Q-3) because their highest representation appears in the lower levels of bogs. The great change in vegetation type, with more emphasis on boreal species (Picea mariana and Pinus banksiana), from Clova (48° 07′ N.) northward to James Bay suggests the Cochrane oscillation influence and subsequent retreat during the ensuing major xerothermic period (Q-3). This period had probably waned by the time the forests were able to invade the James Bay region, thus giving rise to a rather monotonously changeless forest history from lat. 50° 54′ northward (Q-5). Local glaciation is indicated in the bog from Mont Tremblant (Bog 14), where forest history began during the xerothermic period. Fig. 2 presents the highest percentage attained by species at a given latitude, which at a glance divides the species according to latitudinal preference, suggesting temperature control.Since the region about James Bay was covered by the sea following northward wasting of the ice, forest history here begins later than in the areas located above elevation of submergence. Radiocarbon dating of the peat from the bottom level of a bog near Rupert River (51° 27′ N., 78° 32′ W.) places the beginning of organic sediment accumulation at 2350 ± 200 years. This marks the time when marine waters withdrew from the region. Hemlock must have been quite abundant northward to Lac Shaw bog (46° 19′ N.), but reached a pollen representation of 7% even at Lac Mazanaskwa bog (47° 07′ N.). The decline of the white–red pine group on the northern half of the Shield suggests that the muskeg condition north of Clova is due to more recent paludification and more moist climate following the warm–dry period (Q-3). This conclusion is also supported by the prominent rise of Picea mariana. Evidence of tundra conditions was found only in bogs 1, 3, 6, 9, 10, and 12.


1954 ◽  
Vol 86 (4) ◽  
pp. 167-168 ◽  
Author(s):  
H. C. Coppel

In collecting sawfly eggs, larvae, and cocoons for propagating beneficial insects at the Belleville laboratory, a heavy infestation of a pine sawfly, Neodiprion nanulus Schedl, was discovered in 1942 nine miles north of Belleville, on a 25-year-old plantation of red pine, Pinus resinosa Ait.; Scots pine, Pinus sylvestris L.; and jack pine, Pinus banksiana Lamb.From samples of the eggs collected in the spring of 1943, no parasites emerged.


1978 ◽  
Vol 2 (3) ◽  
pp. 83-85 ◽  
Author(s):  
Robert K. Shepard

Abstract A single ice storm caused heavy damage to loblolly pine (Pinus taeda L.) stands row-thinned during the preceding year, but more than 200 undamaged trees per acre were left in all stands. A second ice storm the following year virtually destroyed half of the stands and left only a marginal number of trees in those remaining. A stand thinned from below suffered only light damage.


1969 ◽  
Vol 45 (6) ◽  
pp. 434-440 ◽  
Author(s):  
M. J. Holst ◽  
C. C. Heimburger

The most commonly planted exotic conifers in Canada are Norway spruce (Picea abies (L.) Karst.) and Scots pine (Pinus sylvestris L.) Norway spruce has its highest potential on acid soils in high precipitation areas where it is more productive than the local spruce and fir mixture. Extensive plantations of Norway spruce have not been established because of its susceptibility to attack by white pine weevil. A number of provenance experiments have been established, and selection and breeding for resistance to the white pine weevil appear promising.Scots pine has not been favoured for timber production in Canada mainly because most early seed imports came from poorly formed stands in western Germany. Rapid early growth and green foliage in early winter led to extensive cultivation of these German types for Christmas trees. A limited number of stands from Poland and White Russia, and nearly all the Scots pine from Estonia-Latvia (Riga Pine) are well formed and are recommended for timber production, but not for the growing of Christmas trees. On less fertile sites, Scots pine grows more rapidly than red pine but, at least in the first 20 years, it does not grow as well as jack pine. Selected provenances of Scots pine hold much promise in the prairie region and in the boreal forest.Other exotic spruces have not been widely planted in Canada so very little is known about their silvicultural potential and ecological amplitude. Combined species and provenance trials have been planted recently to remedy this situation. A hybrid between Serbian and black spruce growing at Chalk River, Ontario has grown more rapidly than either parental species. Other species hybrids have been made, but are not yet assessed.In an attempt to develop a hard pine of wider ecological amplitude than red pine, species hybrids have been made between Scots pine, Japanese red pine and varieties of Pinus nigra. These are promising on rich soils in southern Ontario and might be extended further to the north and to poorer acid soils by using selected provenances for the breeding work. Pitch pine has been successfully crossed with P. taeda and P. radiata in an attempt to improve the productivity and potential of pitch pine.


2013 ◽  
Vol 93 (1) ◽  
pp. 25-31 ◽  
Author(s):  
Michael T. Dumas ◽  
Gaston Laflamme

Heterobasidion irregulare is the scientific name for the North American fungal species that was previously known as H. annosum (P-type) and Fomes annosus. In eastern Canada, the pathogen is found mainly in red pine plantations in southern Ontario and Quebec, where it causes tree mortality. There is no registered control method currently available for this disease in Canada. Phlebiopsis gigantea is a saprophytic basidiomycete successfully used and registered as a biological control agent in several European countries. In order to register a control product in Canada, its efficacy must be demonstrated under field conditions. Trials were performed with two Canadian isolates of P. gigantea in four red pine plantations in Ontario. The mean diameters of treated stumps ranged from 29 to 35 cm. After 2 mo, all 238 stumps treated were free of disease, while 12% of the 120 untreated stumps were colonized by the pathogen. The two formulations without P. gigantea did not prevent the colonization of the stumps by either P. gigantea or H. irregulare. These results show that the two Canadian isolates of P. gigantea can prevent colonization of red pine stumps by H. irregulare and provide support for the registration of P. gigantea as a biocontrol agent in eastern Canada.


1993 ◽  
Vol 125 (6) ◽  
pp. 1003-1010 ◽  
Author(s):  
D.W.A. Hunt ◽  
G. Lintereur ◽  
S.M. Salom ◽  
K.F. Raffa

AbstractThe weevils Hylobius radicis Buchanan and Hylobius pales (Herbst) survived to adulthood more frequently, developed more rapidly, and weighed more as adults when reared on diet containing ground phloem from Scots pine, Pinus sylvestris L., or red pine, Pinus resinosa Aiton, than from jack pine, Pinus banksiana Lamb., or eastern white pine, Pinus strobus L. In feeding tests, both weevils preferred Scots pine, although jack pine was preferred over red and white pine. When reared on diets containing phloem from red pines which had received various amounts of nitrogenous fertilizer, H. radicis and H. pales performed significantly better at elevated concentrations of nitrogen. Hylobius radicis adults exhibited a feeding preference for twigs from red pines containing elevated nitrogen concentrations.


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