The Seasonal Development of a Species of Conophthorus (Hopkins) (Coleoptera: Scolytidae) in the Shoots of Jack Pine, Pinus banksiana (Lamb.), in Ontario

1961 ◽  
Vol 93 (10) ◽  
pp. 936-940 ◽  
Author(s):  
H. Herdy ◽  
J. B. Thomas
Keyword(s):  
Pinus Radiata ◽  
Pinus Banksiana ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
Host Tree ◽  
Seasonal Development ◽  
Monterey Pine ◽  
Second Year

Two publications dealing with the seasonal development of species of Conophthorus have appeared in recent years. Lyons (1956) reported on a study of C. resinosae Hopk. in red pine, Pinus resinosa Ait., in Ontario, whereas Ruckes (1958) gave the details of his observations on C. radiatae Hopk. in Monterey pine, Pinus radiata D. Don, in California. Both species attack the developing cones of the host tree, although Lyons found that C. resinosae would develop in the shoots of red pine, and occasionally attacked the second-year cones of jack pine as well. The jack pine-inhabiting species, however, has been found almost exclusively in the shoots; only seven second-year cones that had been mined were collectcd during two years of investigation.

Preference of Tomicus piniperda (Coleoptera: Scolytidae) parent adults and shoot-feeding progeny adults for three pine species

2001 ◽  
Vol 133 (3) ◽  
pp. 343-353 ◽  
Author(s):  
Nathan W. Siegert ◽  
Deborah G. McCullough
Keyword(s):  
Pinus Banksiana ◽  
Host Preference ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
Choice Test ◽  
Tomicus Piniperda ◽  
Scotch Pine ◽  
Laboratory Bioassay ◽  
Pine Shoot Beetle

AbstractHost preference of the pine shoot beetle, Tomicus piniperda (L.), was investigated in two laboratory choice test studies using red pine (Pinus resinosa Ait.) (Pinaceae), jack pine (Pinus banksiana Lamb.), and Scotch pine (Pinus sylvestris L.). Host preference of parent adult beetles was evaluated using freshly cut, similarly sized logs in a wind tunnel. Parent beetles colonized Scotch pine logs significantly more often when given a choice of Scotch pine and either red pine or jack pine logs, but did not show a preference when presented with red pine and jack pine logs. Host preference of progeny adults was tested in a laboratory bioassay using current-year pine shoots. Shoot-feeding progeny adults initiated tunnels in jack pine shoots significantly more often than in Scotch pine and red pine shoots, and preferred Scotch pine over red pine shoots. Shoots with diameters of 0.4–0.5 cm were attacked most frequently, regardless of species. Results suggest that the two North American pines are suitable hosts, but T. piniperda may be most likely to colonize Scotch pine, a European species. Efforts to detect or monitor T. piniperda populations in the Great Lakes and northeastern regions should focus on areas with abundant Scotch pine brood material. Progeny that emerge from brood material, however, may be as likely to shoot-feed in jack pine as in Scotch pine.

Notes on Leconte's Sawfly

1952 ◽  
Vol 84 (2) ◽  
pp. 59-61
Author(s):  
A. S. West
Keyword(s):  
Life History ◽  
Pinus Banksiana ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
Pine Needles ◽  
Pine Sawfly ◽  
Neodiprion Lecontei ◽  
Significant Damage

Leconte's sawfly or the red-headed pine sawfly (Neodiprion lecontei Fitch) is a common insect attacking pines in Ontario. Plantations red pine are almost invariably attacked from the time the trees have reached two to four feet in height. Periodically epidemic populations cause significant damage. The life history and habits of the species have heen described by Middleton (2) who states that this insect attacks practically all species of pine as bell as larch. Schaffner (3) also indicates that the larvae feed on a wide variety of pine and occasionally on other conifers. Red pine (Pinus resinosa Ait.) is undoubtedly the usual host, although in Ontario jack pine (Pinus banksiana Lamb.) is sometimes attacked. In 1946 evidence was secured to show that jack pine needles may be selected for oviposition even in an area where red pine foliage is plentiful. (Figure 1).

COLEOSPORIUM VIBURNI ON JACK PINE AND ITS RELATIONSHIP WITH C. ASTERUM

1966 ◽  
Vol 44 (9) ◽  
pp. 1117-1120
Author(s):  
G. B. Ouellette
Keyword(s):  
Pinus Banksiana ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
Coleosporium Asterum

Through inoculation tests in the greenhouse and in the field, the previously unknown 0 and I stages of Coleosporium viburni Arth. are shown to occur on jack pine (Pinus banksiana Lamb.). These stages are described and differences in aeciospore morphology which permit distinction on pine of this rust from Coleosporium asterum (Diet.) Syd. are discussed. The description of C. asterum is amended to include differences in aeciospore size between collections on jack and red pine (Pinus resinosa Ait.). The known distribution of C. viburni is summarized.

Notes on the Parasites of Neodiprion nanulus Schedl (Hymenoptera: Tenthredinidae)

1954 ◽  
Vol 86 (4) ◽  
pp. 167-168 ◽  
Author(s):  
H. C. Coppel
Keyword(s):  
Pinus Sylvestris ◽  
Scots Pine ◽  
Pinus Banksiana ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
Pine Sawfly ◽  
Beneficial Insects ◽  
Heavy Infestation

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.

scholarly journals Resistance of Pinus banksiana to the European race of Gremmeniella abietina

2005 ◽  
Vol 81 (2) ◽  
pp. 49-55 ◽  
Author(s):  
G. Laflamme ◽  
R. Blais
Keyword(s):  
Distinctive Feature ◽  
Pinus Banksiana ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
The North ◽  
Pine Seedlings ◽  
Pine Trees ◽  
European Race ◽  
Low Incidence

In the early 1980s, more than 90% of mortality caused by Gremmeniella abietina, European race, was recorded in red pine (Pinus resinosa) plantations 200 km northwest of Montreal, Quebec, Canada. Surrounding jack pines (Pinus banksiana) did not appear to be affected. Consequently, foresters began to plant the affected areas with jack pine seedlings. In 1988, plots of 100 jack pines were established in three of the four selected plantations. As reference, red pine seedlings were planted in 1989 under similar conditions in the fourth plantation. Observations were carried out annually from 1989 to 1992. Mortality of red pine seedlings reached 70% in 1992 while all jack pines on the three experimental sites were free of the disease except for a tip blight, a distinctive feature allowing race identification in the field. The North American race symptoms were present at a very low incidence, but began to increase on site I in 1992. More than 10 years after planting, the jack pine trees still show resistance to the European race of G. abietina while all the red pines died.

NEW RECORDS AND NOTES OF SALTATORIA (ORTHOPTERA) IN ONTARIO

1942 ◽  
Vol 74 (6) ◽  
pp. 97-98 ◽  
Author(s):  
F. A. Urquhart
Keyword(s):  
North Carolina ◽  
Pinus Banksiana ◽  
New Records ◽  
Pinus Strobus ◽  
Pinus Resinosa ◽  
Jack Pine ◽  
Red Pine ◽  
White Pine ◽  
Southern Ontario

Oecanthus pini Beutenmuller. Since O. pini is known to range from Massachusetts west to Ohio and south to North Carolina, it is not surprising to find it in extreme southern Ontario. The specimens here recorded were found on white pine (Pinus strobus L.), red pine (Pinus resinosa Sol. and jack pine (Pinus Banksiana Lam.) in an area devoted to reforestation.

THE SEED PRODUCTION CAPACITY AND EFFICIENCY OF RED PINE CONES (PINUS RESINOSA AIT.)

1956 ◽  
Vol 34 (1) ◽  
pp. 27-36 ◽  
Author(s):  
L. A. Lyons
Keyword(s):  
Seed Production ◽  
Production Efficiency ◽  
Production Capacity ◽  
Pinus Resinosa ◽  
Proximal Part ◽  
Red Pine ◽  
First Year ◽  
Tree Crown ◽  
Second Year ◽  
Pine Cones

The seed capacity of red pine cones varies from about 30 to over 110, depending on the size of the cone and its position in the tree crown, and is determined by the number of ovules that are structurally complete at the time of pollination. These ovules occur in a central "productive" region and constitute less than one-half of the total. The remaining ovules, most: of which are in the proximal part of the cone, never become structurally perfect, and do not contribute to seed production. Abortion of ovules in the productive region usually reduces seed production efficiency to 50–60%, and is accompanied mainly by withering of the nucellus in the first year and failure to produce archegonia early in the second year. The extent of ovule abortion during the first year varies indirectly with cone size, seed capacity, and height in tree.

scholarly journals Genetic Differentiation of Jack Pine (Pinus banksiana) and Red Pine (P. resinosa) Populations From Metal Contaminated Areas in Northern Ontario (Canada) Using ISSR Markers

2008 ◽  
Vol 57 (1-6) ◽  
pp. 333-340 ◽  
Author(s):  
M. Ranger ◽  
K. K. Nkongolo ◽  
P. Michael ◽  
P. Beckett
Keyword(s):  
Genetic Diversity ◽  
Pinus Banksiana ◽  
Metal Accumulation ◽  
Gene Diversity ◽  
Jack Pine ◽  
Issr Markers ◽  
Red Pine ◽  
Northern Ontario ◽  
Polymorphic Loci ◽  
Information Index

Abstract Metal accumulation in soil and plant tissues has caused severe ecological damage in forest ecosystems in the Sudbury region. The main objective of the present study was to determine the levels of genetic diversity in jack and red pine populations growing in metal contaminated and uncontaminated areas. Newly introduced populations were compared to 40 to 60 old populations. For jack pine, the percentage of polymorphic loci (P %) ranged from 14.6% to 45.8% with a mean of 31.6%. Nei’s gene diversity (h) varied from 0.046 to 0.169 with an average of 0.100, and Shannon’s index (I) ranged from 0.070 to 0.250 with an average of 0.153. The level of genetic variation was much lower in the red pine populations. For this species, the level of polymorphic loci varied from 4.55% to 27.27%. The mean for Nei’s gene diversity and Shannon’s information index, were 0.034 and 0.053, respectively. The highest genetic diversity values were observed in new plantations being developed by the Sudbury reforestation program. Overall, the genetic distance among the Pinus banksiana populations revealed that all the populations analyzed were genetically close to each other. There was no association between metal accumulation and genetic diversity for both species.

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