|This article may require cleanup to meet Wikipedia's quality standards. The specific problem is: likely markup problems with references. (September 2014)|
Silviculture is the practice of controlling the establishment, growth, composition, health, and quality of forests to meet diverse needs and values. The name comes from the Latin silvi- (forest) + culture (as in growing). The study of forests and woods is termed silvology. Silviculture also focuses on making sure that the treatment(s) of forest stands are used to preserve and to better their productivity.
Generally, silviculture is the science and art of growing and tending forest crops, based on a knowledge of silvics, i.e., the study of the life history and general characteristics of forest trees and stands, with particular reference to locality factors (Ford-Robertson 1971). More particularly, silviculture is the theory and practice of controlling the establishment, composition, constitution, and growth of forests. No matter how forestry as a science is constituted, the kernel of the business of forestry is silviculture, as it includes direct action in the forest, and in it all economic objectives and technical considerations ultimately converge (Köstler 1956). The kernel of silviculture is regeneration.
Suggestions for how best to go about the job, presented by Jeglum et al. (2003), though aimed primarily at the boreal forest in Ontario, merit wider consideration. The 110-page publication describes Best Management Practices, first by general principles, then by sensitive sites. Illustrations are plentiful and are well chosen to complement this excellent text.
To some the distinction between forestry and silviculture is that silviculture is applied at the stand level and forestry is broader. For example John D. Matthews says "complete regimes for regenerating, tending, and harvesting forests" are called "silvicultural systems".
So active management is required for silviculture, whereas forestry can be natural, conserved land without a stand level treatment being applied. A common taxonomy divides silviculture into regenerating, tending and harvesting techniques.
- 1 Silvicultural systems
- 2 Regeneration
- 3 Artificial regeneration
- 4 Forest tree nurseries
- 5 Forest tree plantations
- 6 Competition
- 7 Tending
- 8 Growth and yield
- 9 Common methods of harvesting
- 9.1 Clearcut harvesting
- 9.2 Clearcutting
- 9.3 Coppicing
- 9.4 Direct seeding
- 9.5 Group selection
- 9.6 Méthode du contrôle
- 9.7 Patch cut
- 9.8 Row and broadcast seeding
- 9.9 Seed-tree
- 9.10 Selection systems
- 9.11 Shelter spot seeding
- 9.12 Shelterwood
- 9.13 Shelterwood systems
- 9.14 Single-tree selection
- 9.15 Spot seeding
- 9.16 Strip cutting
- 9.17 Underplanting
- 9.18 Variable retention
- 10 Mortality
- 11 Advance growth
- 12 Site preparation
- 13 See also
- 14 References
- 15 External links
Various “silvicultural systems” have been devised to effect regeneration. In British Columbia, for example, 4 silvicultural systems are used: (1) clearcutting, (2) seed-tree, (3) shelterwood, and (4) selection. Clearcutting, though the most efficient and least expensive way of harvesting wood, may create difficulties that impede the establishment of regeneration. Obtaining natural regeneration of white spruce in Alaska and boreal Canada after clearcutting has proved to be difficult (Lees 1970, Stiell 1976, Greene et al. 1999). In addition, white spruce that are outplanted in the open in severe boreal climates without a modicum of protective “nursing” can stagnate for decades (Sutton 1992).
Regeneration is basic to the continuation of forest, as well as to the afforestation of treeless land. Regeneration can take place through self-sown seed (“natural regeneration”), by artificially sown seed, or by planted seedlings. In either case, the performance of regeneration depends on its growth potential and the degree to which its environment allows the potential to be expressed (Grossnickle 2000). Seed, of course, is needed for all regeneration modes, both for natural or artificial sowing and for raising planting stock in the nursery.
Natural regeneration is:
"Human-assisted natural regeneration" means establishment of a forest age class from natural seeding or sprouting in an area after harvesting in that area through selection cutting, shelter (or seed-tree) harvest, soil preparation, or restricting the size of a clear-cut stand to secure natural regeneration from the surrounding trees.
The process of natural regeneration involves the renewal of forests by means of self-sown seeds, root suckers, or coppicing. In natural forests, conifers rely almost entirely on regeneration through seed. Most of the broadleaves, however, are able to regenerate by the means of emergence of shoots from stumps (coppice) and broken stems.
Any seed, self-sown or artificially applied, requires a seedbed suitable for securing germination.
In order to germinate, a seed requires suitable conditions of temperature, moisture, and aeration. For seeds of many species, light is also necessary, and facilitates the germination of seeds in other species (Schopmeyer 1974), but spruces are not exacting in their light requirements, and will germinate without light. White spruce seed germinated at 35 °F (1.7 °C) and 40 °F (4.4 °C) after continuous stratification for one year or longer and developed radicles < 6 cm long in the cold room (MacArthur and Fraser 1963). When exposed to light, those germinants developed chlorophyll and were normally phototropic with continued elongation.
For survival in the short and medium terms, a germinant needs: a continuing supply of moisture; freedom from lethal temperature; enough light to generate sufficient photosynthate to support respiration and growth, but not enough to generate lethal stress in the seedling; freedom from browsers, tramplers, and pathogens; and a stable root system. Shade is very important to the survival of young seedlings (Arnott 1974, Alexander 1984). In the longer term, there must be an adequate supply of essential nutrients and an absence of smothering.
In undisturbed forest, decayed windfallen stemwood provides the most favourable seedbed for germination and survival, moisture supply being dependable, and the elevation of seedlings somewhat above the general level of the forest floor reduces the danger of smothering by leaves and snow-pressed minor vegetation; nor is such a microsite likely to be subject to flooding. Advantages conferred by those microsites include: more light, higher temperstures in the rooting zone, and better mycorrhizal development (Baldwin 1927, Mork 1933, Rowe 1955). In a survey in the Porcupine Hills, Manitoba, 90% of all spruce seedlings were rooted in rotten wood (Phelps 1940a, b).
Mineral soil seedbeds are more receptive than the undisturbed forest floor (Alexander 1958), and are generally moister and more readily rewetted than the organic forest floor. However, exposed mineral soil, much more so than organic-surfaced soil, is subject to frost-heaving and shrinkage during drought. The forces generated in soil by frost or drought are quite enough to break roots (Sutton 1991).
The range of microsites occurring on the forest floor can be broadened, and their frequency and distribution influenced by site preparation. Each microsite has its own microclimate. Microclimates near the ground are better characterized by vapour pressure deficit and net incident radiation, rather than the standard measurements of air temperature, precipitation, and wind pattern (Alexander 1984).
Aspect is an important component of microclimate, especially in relation to temperature and moisture regimes. Germination and seedling establishment of Engelmann spruce were much better on north than on south aspect seedbeds in the Fraser Experimental Forest, Colorado; the ratios of seeds to 5-year-old seedlings were determined as 32:1, 76:1, and 72:1 on north aspect bladed-shaded, bladed-unshaded, and undisturbed-shaded seedbeds, respectively (Alexander 1983). Clearcut openings of 1.2 ha to 2.0 ha adjacent to an adequate seed source, and not more than 6 tree heights wide, could be expected to secure acceptable regeneration (4,900, 5-year-old trees/ha), whereas on undisturbed-unshaded north aspects, and on all seedbed treatments tested on south aspects, seed to seedling ratios were so high that the restocking of any clearcut opening would be questionable.
At least 7 variable factors may influence seed germination: (1) seed characteristics, (2) light, (3) oxygen, (4) soil reaction (ph), (5) temperature, (6) moisture, and (7) seed enemies (Baldwin 1942). Moisture and temperature are the most influential, and both are affected by exposure. The difficulty of securing natural regeneration of Norway spruce and Scots pine in northern Europe led to the adoption of various forms of reproduction cuttings that provided partial shade or protection to seedlings from hot sun and wind (Baldwin 1933). The main objective of echeloned strips or border-cuttings with northeast exposure was to protect regeneration from overheating, and was originated in Germany and deployed successfully by Alarik (1925) and others in Sweden. On south and west exposures, direct insolation and heat reflected from tree trunks often result in temperatures lethal to young seedlings (Hartley 1918), as well as desiccation of the surface soil, which inhibits germination. The sun is less injurious on eastern exposures because of the lower temperature in the early morning, related to higher humidity and presence of dew.
Baldwin (1933), after noting that summer temperatures in North America are often higher than those in places where border-cuttings have been found useful, reported the results of a survey of regeneration in a stand of red spruce plus scattered white spruce that had been isolated by clearcutting on all sides, so furnishing an opportunity for observing regeneration on different exposures in this old-field stand at Dummer, New Hampshire. The regeneration included a surprisingly large number of balsam fir seedlings from the 5% stand component of that species. The maximum density of spruce regeneration, determined 4 rods (20 m) inside from the edge of the stand on a North 20°E exposure, was 600,000/ha, withalmost 100,000 balsam fir seedlings.
A prepared seedbed remains receptive for a relatively short period, seldom as long as 5 years, sometimes as short as 3 years. Seedbed receptivity on moist, fertile sites decreases with particular rapidity, and especially on such sites, seedbed preparation should be scheduled to take advantage of good seed years. In poor seed years, site preparation can be carried out on mesic and drier sites with more chance of success, because of the generally longer receptivity of seedbeds there than those on moister sites (Eis and Inkster 1972). Although an indifferent seed year can suffice if seed distribution is good and environmental conditions favourable to seedling germination and survival (Noble and Ronco 1978), small amounts of seed are particularly vulnerable to depredation by small mammals (Radvanyi 1970). Considerable flexibility is possible in timing site preparation to coincide with cone crops. Treatment can be applied either before any logging takes place, between partial cuts, or after logging (Coates et al. 1994). In cut and leave strips, seedbed preparation can be carried out as a single operation, pre-scarifying the leave strips, post-scarifying the cut strips (Gilmour and Konishi 1965).
Broadcast burning is not recommended as a method of preparing sites for natural regeneration, as it rarely exposes enough mineral soil to be sufficiently receptive, and the charred organic surfaces are a poor seedbed for spruce (Ackerman 1957; Zasada 1985, 1986; Zasada and Norum 1986). A charred surface may get too hot for good germination and may delay germination until fall, with subsequent overwinter mortality of unhardened seedlings (Bell 1991). Piling and burning of logging slash, however, can leave suitable exposures of mineral soil (Coates et al. 1994).
Season of planting
The classical silvicultural literature unanimously advocates spring as the time to plant bareroot stock, with lifting and outplanting taking place while the trees are still apparently dormant (Sutton 1984). This view, in which spring planting is implicit, was epitomized by Toumey and Korstian (1942): “Almost without exception the most favourable time for ... planting is 2 weeks or more before buds [of the planting stock] begin their growth”. Soil moisture conditions are generally favourable at the time when the growing season is about to begin, while dormant stock is less subject to mechanical injury and physiological shock (Stiell 1976).
If the size of the planting program allows, there is little doubt that such scheduling would be advantageous in that it satisfies one, and commonly 2, of the factors essential for success: (1) the use of planting stock that is physiologically capable of responding to a growth environment at planting, and (2) planting when site factors favour tree survival and growth. The 3rd factor a good planting job, and although desirable in all plantings, is probably somewhat less critical in conventional spring plantings than at other times. If, however, a planting program cannot be completed in this way, there are other options: conventional fall planting with fresh-lifted stock; summer planting with fresh-lifted stock; and spring and summer planting with stored spring-lifted or fall-lifted stock (Sutton 1984).
Conventional spring planting with fresh spring-lifted stock
In the context of regeneration silviculture, “spring”, “summer”, etc. lack precise meaning. Typically, the spring planting season begins as soon as lifting becomes possible in the nursery, and ends with the completion of the program. At this time, planting stock is physiologically attuned to the oncoming growing season, and the outplant has the whole of that season in which to establish its root system before it is challenged by any frost heaving. In practice, ideals are seldom attained. That stock is normally dormant when spring-planted is a widespread fallacy. Active growth is commonly obvious at the time of planting, but in any case the metabolic activity increases in planting stock before the tops give visible expression to this. The difficulty of obtaining, in quantity, spring-lifted stock in dormant condition increases with increasing continentality of climate. In many areas, the period of spring-like weather is unreliable and often short. As well, the soil moisture advantage claimed for spring planting is also insecurely founded. Soils that are sandy or gravelly, and shallow soils of any texture are highly dependent on current weather due to their limited available water capacities. Nor will a plentiful supply of soil moisture benefit an outplant whose roots are enveloped in anaerobic and/or cold soil, and mortality of trees outplanted into soil colder than about 6 °C may be excessive (Sutton 1968, 1969). Flushing increases the vulnerability of planting stock to both physiological stress (because of increased water requirements and reduced root growth capacity) and mechanical damage, which probably accounts for the commonly asserted superiority of early spring over late spring planting.
In fact, the spruces may be planted not only throughout the spring planting period provided that the period of most active shoot elongation is avoided, but virtually throughout the whole growing season, with little loss of performance other than some reduction in increment. Mullin’s (1971) study at Midhurst in southern Ontario illustrates both the success with which white spruce can be planted throughout the period in question and the need to minimize stresses on the planting stock. Mullin used 3+0 stock from regular shipping beds in a series of 6 weekly plantings beginning with apparently dormant trees on 3 May and ending on 7 June, by which time the new leading shoots were several centimetres long. Trees were lifted with and without root dipping, planted on the day of lifting after their root systems had been exposed for 0, 1, 2, or 3 hours. Whereas 2nd year survival in the control (root exposure = 0) condition varied little among the 6 plantings, with averages of 83.5% +/- 4.7% for root-dipped trees and 77.2 +/- 7.0% for non-dipped, mortality rates among root-exposed stock were very much more variable. For instance, 2nd-year survival among root-dipped trees whose root systems had been exposed for 1 hour varied from 17% to 84%.
Conventional fall planting with fresh-lifted stock
The fall planting season is generally considered to begin when nursery stock has hardened off and soil moisture reserves have been replenished by autumnal rain.It then continues until the planting program has been completed or is terminated by freeze-up or heavy snow. The advantages of fall planting were once considered “To outweigh those of spring so certainly” that in the National Forests of the Lake States almost all planting was done in the fall (Kittredge 1929), but in spite of some success, operational fall plantings in North America have tended to be less successful than operational spring plantings (LeBarron et al. 1938). On certain sites, a major disadvantage of fall planting is that the root systems of outplants have little time in which to become firmly anchored before being subjected to frost heaving. Such plants are also vulnerable to “winter browning”, which in fact may occur in the fall soon after planting, especially among stock having high shoot:root ratios (Rudolf 1950). Relationships between dormancy progression and physiological condition, including root-growth capacity, are much less clear in the spruces than in the pines, but certainly there is good evidence (Baldwin 1938; Mullin 1968; Sinclair and Boyd 1973; McClain 1975, 1979) that, in the absence of frost heaving, plantings of spruces can be just as successful in fall as in spring.
Summer planting with fresh-lifted stock
Conceptually and logistically, the simplest way of extending the conventional planting season is to extend lifting and planting of fresh stock through summer until the planting program has been competed. There is ample evidence that spruces may be planted successfully throughout the summer, not least the notable operational success of Marek (Personal communication, 1985, George T. Marek, R.P.F., Beardmore, Ontario, Ontario Ministry of Natural Resources) in northwestern Ontario: “the success of my plantations is primarily due to different strategies and cool storaging in Beardmore. I have planted all species from spring to late fall, throughout the summer on a large scale, without any difficulties”. Summer planting has also been successful in a number of research studies with white spruce, e.g., Crossley 1956; Ackerman and Johnson 1962; Decie 1962 cited by Revel and Coates 1976; Burgar and Lyon 1968; Mullin 1971, 1974; Revel and Coates 1976. Success depends on minimizing stresses to planting stock at all stages from lifting through planting and on planting when site conditions are conducive to survival and growth.
Spring and summer planting with stored stock
Refrigerated storage of planting stock has been developed largely with the aim of overcoming problems experienced in using flushed planting stock. Storage provides a means of holding stock for use when fresh stock is either unavailable or at a stage of development that renders it unsuitable for planting. It also offers possibilities of manipulating the physiological condition of the stock. However, there are problems associated with storage, e.g., mold, cold injury, desiccation, and depletion of food reserves. The rate of deterioration depends very much on the physiological condition of the planting stock at the time of lifting, as well as on the storage environment and duration of storage. In attempts to devise safe schedules for spring-lifting of stock for frozen storage, Mullin (1978) used a base of 0 °C and accumulated daily maximum soil temperatures at 15 cm depth to calculate degree days (DD). He interpreted the evidence to mean that white spruce destined for frozen storage should have accumulated no more than 50 DD before being lifted. With regard to cool-stored, spring-lifted stock, the main ingredients for success are lifting before flushing has begun, prevention of desiccation, maintenance of a constant temperature within 1 or 2 degrees of freezing, minimization of mold by good temperature control and sanitation, avoidance of crushing and other mechanical damage, and avoidance of longer than necessary periods of storage.
Mullin and Forcier (1976) and Mullin and Reffle (1980) examined the effects of spring-lifting date and planting date on several species, including 3+0 white spruce after frozen storage, with fresh-lifted controls planted on each planting date for comparison. In all plantings, the earliest (2 May) lifting gave highest average second-year survival in all species. In another study, Mullin (1978) found that outplantings of frozen-stored 3+0 white spruce were consistently successful to the end of July only with the earliest -lifted (25 April) stock. Sutton (1982) also used 3+0 white spruce in outplanting every 2 weeks from the end of June through the growing season in 3 successive years on a variety of sites in northern Ontario. Despite variation in planting stock, poor storage environments and adverse weather, 4th-year results showed a consistent pattern of reasonable survival and growth rates among trees planted through July, with a rapid decline in performance of trees planted thereafter. Overwinter storage of stock has also been employed. It has the advantage of lifting stock at the end of the growing season when physiological processes are invoking natural dormancy. Time of fall lifting was investigated by Mullin and Parker (1976) along with overwinter storage temperature to determine their effects on the performance of spring-planted 3+0 white spruce. There were 5 lifts, weekly from 19 October through 16 November, after which frozen ground put a stop to lifting. Two storage temperatures were used, -18 °C and -4 °C. Nearly all of the trees stored at -18 °C died. The other stock was planted in shallow furrows in sparsely sodded field of loamy sand on 12 April, 17 May, and 14 June along with fresh-lifted stock on each date. Fresh and stored white spruce gave comparable results in plantings extended into mid-June in the Midhurst area of Ontario.
Natural refrigerated overwinter storage has been used in root cellars and snow caches. Using natural refrigeration in root cellar storage, Jorgensen and Stanek (1962) kept 3+0 and 2+2 white spruce in dormant condition for 6 months without apparent detriment to performance after outplanting. Moreover, the stock was highly resistant to spring frost damage. Natural cold storage for overwintering 3+0 and 2+2 white spruce was also used by Mullin (1966). Unlike Jorgensen and Stanek’s (1962) stock, which was raised 550 km to the south of where it was planted, Mullin’s stock was raised in a nursery at about the same latitude as the planting site; the stock experienced inside-bale temperatures down to -15 °C in mid-winter, but still showed first- and second-year survival rates of 85.9% and 65.9%, respectively, compared with 91.4% and 76.2%, respectively, for fresh-lifted stock. However, Mullin’s stored stock was much more damaged by spring frost than was fresh-lifted stock and it “showed a reduction in vigour as measured in terms of survival, susceptibility to damage and growth”.
With a view to reducing the time needed to produce planting stock, experiments were carried out with white spruce and 3 other coniferous species from Wisconsin seed in the longer, frost-free growing season in Florida, 125 vs. 265 days in central Wisconsin and northern Florida, respectively (Anon. 1961). As the species studied are adapted to long photoperiods, extended daylengths of 20 hours were applied in Florida. Other seedlings were grown under extended daylength in Wisconsin and with natural daylength in both areas. After 2 growing seasons, white spruce under long days in Florida were about the same as those in Wisconsin, but twice as tall as plants under natural Wisconsin photoperiods. Under natural days in Florida, with the short local photoperiod, white spruce was severely dwarfed and had a low rate of survival. Black spruce responded similarly. After 2 growing seasons, long day plants of all 4 species in Florida were well balanced, with good development of both roots and shoots, equalling or exceeding the minimum standards for 2+1 and 2+2 outplanting stock of Lake States species. Their survival when lifted in February and outplanted in Wisconsin equalled that of 2+2 Wisconsin-grown transplants. Artificial extension of the photoperiod in the northern Lake States greatly increased height increment of white and black spruces in the second growing season.
Optimum conditions for seedling growth have been determined for the production of containerized planting stock (Nienstaedt and Zasada 1990). Alternating day/night temperatures have been found more suitable than a constant temperature; at 400 lumens/m² light regime, a 28 °C/20 °C day/night temperatures have been recommended for white spruce (Pollard and Logan 1976, Carlson 1979, Tinus and McDonald 1979). However, temperature optima are not necessarily the same at different ages and sizes (Tinus and McDonald 1979). Tinus (1984) investigated the effects of combinations of day and night temperature on height, caliper, and dry weight of 4 seed sources of Engelmann spruce. The 4 seed sources appeared to have very similar temperature requirements, with night optima about the same of slightly lower than daylight optima.
Tree provenance is important in artificial regeneration. Good provenance takes into account suitable tree genetics and a good environmental fit for planted / seeded trees in a forest stand. The wrong genotype can lead to failed regeneration, or poor trees that are prone to pathogens and undesired outcomes.
Artificial regeneration has been a more common method involving planting because it is more dependable than natural regeneration. Planting can involve using seedlings (from a nursery), (un)rooted cuttings, or seeds.
Whichever method is chosen it can be assisted by tending techniques also known as intermediate stand treatments.
The fundamental genetic consideration in artificial regeneration is that seed and planting stock must be adapted to the planting environment. Most commonly, the method of managing seed and stock deployment is through a system of defined seed zones, within which seed and stock can be moved without risk of climatic maladaptation (Joyce et al. 2001). Ontario adopted a seed zone system in the 1970s based on Hills’ (1952) site regions and provincial resource district boundaries, but Ontario’s seed zones are now based on homogeneous climatic regions developed with the Ontario Climate Model (Mackey et al. 1996, OMNR 1997). The regulations stipulate that source-identified seedlots may be either a general collection, when only the seed zone of origin is known, or a stand collection from a specific latitude and longitude. The movement of general-collection seed and stock across seed zone boundaries is prohibited, but the use of stand-collection seed and stock in another seed zone is acceptable when the Ontario Climate Model shows that the planting site and place of seed origin are climatically similar. The 12 seed zones for white spruce in Quebec are based mainly on ecological regions, with a few modifications for administrative convenience (Li et al. 1997).
Seed quality varies with source. Seed orchards produce seed of the highest quality, then, in order of decreasing seed quality produced, seed production areas and seed collection areas follow, with controlled general collections and uncontrolled general collections producing the least characterized seed.
When seed is first separated from cones it is mixed with foreign matter, often 2 to 5 times the volume of the seed. The more or less firmly attached membranous wings on the seed must be detached before it is cleaned of foreign matter (Toumey and Korstian 1954). The testa must not incur damage during the dewinging process. Two methods have been used, dry and wet. Dry seed may be rubbed gently through a sieve that has a mesh through which only seed without wings can pass. Large quantities of seed can be processed in dewinging machines, which use cylinders of heavy wire mesh and rapidly revolving stiff brushes within to remove the wings. In the wet process, seed with wings attached are spread out 10 cm to 15 cm deep on a tight floor and slightly moistened throughout; light leather flails are used to free seed from the wings. Wang (1973) described a unique wet dewinging procedure using a cement mixer, used at the Petawawa tree seed processing facility. Wings of white and Norway spruce seed can be removed by dampening the seed slightly before it is run through a fanning mill for the last time (Toumey and Korstian 1954). Any moistened seed must be dried before fermentation or moulding sets in.
A fluorescein diacetate (FDA) biochemical viability test for several species of conifer seed, including white spruce, estimates the proportion of live seed (viability) in a seedlot, and hence the percentage germination of a seedlot. The accuracy of predicting percentage germination was within +/- 5 for most seedlots (Noland et al. 2001). White spruce seed can be tested for viability by an indirect method, such as the fluorescein diacetate (FDA) test (Noland et al. 2001) or ‘Ultra-sound’ (Timonin 1966); or by the direct growth method of ‘germination’. Samples of white spruce seed inspected by Toumey and Stevens (1928) varied in viability from 50% to 100%, but averaged 93%. Rafn (1915) reported 97% viability for white spruce seed.
The results of a germination test are commonly expressed as germinative capacity or a germination percentage, which is the percentage of seeds that germinate during a period of time, ending when germination is practically complete. During extraction and processing, white spruce seeds gradually lost moisture, and total germination increased. Mittal et al. (1987) reported that white spruce seed from Algonquin Park, Ontario, obtained the maximum rate (94% in 6 days) and 99% total germination in 21 days after 14-week pre-chilling. The pre-treatment of 1% sodium hypochlorite increased germinability.
Encouraged by Russian success in using ultrasonic waves to improve the germinative energy and percentage germination of seeds of agricultural crops, Timonin (1966) demonstrated benefits to white spruce germination after exposure of seeds to 1, 2, or 4 minutes of ultrasound generated by an M.S.E. ultrasonic disintegrator with a power consumption of 280 VA and power impact of 1.35 amperes (Tables 3.18 and 3.19, Timonin 1966). However, no seeds germinated after 6 minutes of exposure to ultrasound.
Seed dormancy is a complex phenomenon and is not always consistent within species (Haddon and Winston 1982). Cold stratification of white spruce seed to break dormancy has been specified as a requirement (Wang 1974a, Zasada et al. 1978, Armson and Sadreika 1979, Simpson et al. 2004 ), but Heit (1961) and Hellum (1968) regarded stratification as unnecessary. Cone handling and storage conditions affect dormancy in that cold, humid storage (5 °C, 75% to 95% relative humidity) of the cones prior to extraction seemingly eliminated dormancy by overcoming the need to stratify (Haddon and Winston 1982). Periods of cold, damp weather during the period of cone storage might provide natural cold (stratification) treatment. Once dormancy was removed in cone storage, subsequent kiln-drying and seed storage did not reactivate dormancy.
Haddon and Winston (1982) found a reduction in viability of stratified seeds after 2 years of storage and suggested that stress might have been caused by stratification, e.g., by changes in seed biochemistry, reduced embryo vigor, seed aging or actual damage to the embryo. They further questioned the quality of the 2-year-old seed even though high germination occurred in the samples that were not stratified.
Cold stratification is the term applied to the storing of seeds in (and, strictly, in layers with) a moist medium, often peat or sand, with a view to maintaining viability and overcoming dormancy. Cold stratification is the term applied to storage at near-freezing temperatures, even if no medium is used. A common method of cold stratification, is to soak seed in tap water for up to 24 h, superficially dry it, then store moist for some weeks or even months at temperatures just above freezing (van den Driessche 1969, Santon 1970, Wang 1987). Although Hellum (1968) found that cold stratification of an Alberta seed source led to irregular germination, with decreasing germination with increasing length of the stratification period, Hocking’s (1972) paired test with stratified and nonstratified Alberta seed from several sources revealed no trends in response to stratification. Hocking suggested that seed maturity, handling, and storage needed to be controlled before the need for stratification could be determined. Later, Winston and Haddon (1981) found that the storage of white spruce cones for 4 weeks at 5 °C prior to extraction obviated the need for stratification.
Seed maturity cannot be predicted accurately from cone flotation, cone moisture content, cone specific gravity; but the province of B.C. found embryo occupying 90% + of the corrosion cavity and megagametophyte being firm and whitish in colour are the best predictors for white spruce in B.C. (Kolotelo 1997), and Quebec can forecast seed maturity some weeks in advance by monitoring seed development in relation to heat-sums and the phenological progression of the inflorescence of fireweed (Epilobium angustifolium L.), an associated plant species (Mercier 1991). Cone collection earlier than one week before seed maturity would reduce seed germination and viability during storage (Mercier 1991). Four stages of maturation were determined by monitoring carbohydrates, polyols, organic acids, respiration, and metabolic activity. White spruce seeds require a 6-week post-harvest ripening period in the cones to obtain maximum germinability (Caron et al. 1990), however, based on cumulative degree-days, seed from the same trees and stand showed 2-week cone storage was sufficient (Caron et al. 1993).
Forest tree nurseries
Whether in the forest or in the nursery, seedling growth is fundamentally influenced by soil fertility, but nursery soil fertility is readily amenable to amelioration, much more so than is forest soil.
Nitrogen, phosphorus, and potassium are regularly supplied as fertilizers, and calcium and magnesium are supplied occasionally. Applications of fertilizer nitrogen do not build up in the soil to develop any appreciable storehouse of available nitrogen for future crops (Armson and Carman 1961). Phosphorus and potassium, however, can be accumulated as a storehouse available for extended periods.
Fertilization permits seedling growth to continue longer through the growing season than unfertilized stock; fertilized white spruce attained twice the height of unfertilized (Armson 1966). High fertility in the rooting medium favours shoot growth over root growth, and can produce top-heavy seedlings ill suited to the rigors of the outplant site. Nutrients in oversupply can reduce growth (Stiell 1976, Duryea and McClain 1984) or the uptake of other nutrients (Armson and Sadreika 1979). As well, an excess of nutrient ions can prolong or weaken growth to interfere with the necessary development of dormancy and hardening of tissues in time to withstand winter weather (van den Driessche 1980).
Stock types, sizes and lots
Nursery stock size typically follows the normal curve when lifted for planting stock. The runts at the lower end of the scale are usually culled to an arbitrary limit, but, especially among bareroot stock, the range in size is commonly considerable. Dobbs (1976) and McMinn (1985a) examined how the performance of 2+0 bareroot white spruce related to differences in initial size of planting stock. The stock was regraded into large, medium, and small fractions according to fresh weight. The small fraction (20% of the original stock) had barely one-quarter of the dry matter mass of the large fraction at the time of outplanting. Ten years later, in the blade-scarified site, seedlings of the large fraction had almost 50% greater stem volume than had seedlings of the small fraction. Without site preparation, large stock were more than twice the size of small stock after 10 years.
Similar results were obtained with regraded 2+1 transplants sampled to determine root growth capacity (McMinn 1980, 1984). The large stock had higher RGC as well as greater mass than the small stock fraction.
The value of large size at the time of planting is especially apparent when outplants face strong competition from other vegetation, although high initial mass does not guarantee success. That the growth potential of planting stock depends on much more than size seems clear from the indifferent success of the transplanting of small 2+0 seedlings for use as 2+1 “reclaim” transplants (McMinn 1985a). The size of bareroot white spruce seedlings and transplants also had a major influence on field performance.
The field performance among various stock types in Ontario plantations was examined by Paterson and Hutchison (1989): the white spruce stock types were 2+0, 1.5+0.5, 1.5+1.5, and 3+0. The nursery stock was grown at Midhurst Forest Tree Nursery, and carefully handled through lifting on 3 lift dates, packing, and hot-planting into cultivated weed-free loam. After 7 years, overall survival was 97%, with no significant differences in survival among stock types. The 1.5+1.5 stock with a mean height of 234 cm was significantly taller by 18% to 25% than the other stock types. The 1.5+1.5 stock also had significantly greater dbh than the other stock types by 30-43%. The best stock type was 57 cm taller and 1 cm greater in dbh than the poorest. Lifting date had no significant effect on growth or survival.
High elevation sites in British Columbia’s southern mountains are characterized by a short growing season, low air and soil temperatures, severe winters, and deep snow. The survival and growth of Engelmann spruce and subalpine fir outplanted in 3 silvicultural trials on such sites in gaps of various sizes were compared by Lajzerowicz et al. (2006). Survival after 5 or 6 years decreased with smaller gaps. Height and diameter also decreased with decreasing size of gap; mean heights were 50 cm to 78 cm after 6 years, in line with height expectations for Engelmann spruce in a high-elevation planting study in southeastern British Columbia (Thompson 1995). In the larger gaps (≥1.0 ha), height increment by year 6 was ranging from 10 cm to 20 cm. Lajzerrowicz et al. Concluded that plantings of conifers in clearcuts at high elevations in the southern mountains of British Columbia are likely to be successful, even close to timberline; and group selection silvicultural systems based on gaps 0.1 ha or larger are also likely to succeed. Gaps smaller than 0.1 ha do not provide suitable conditions for obtaining adequate survival or for growth of outplanted conifers.
Planting stock, “seedlings, transplants, cuttings, and occasionally wildings, for use in planting out” (Ford-Robertson 1971), is nursery stock that has been made ready for outplanting.The amount of seed used in white spruce seedling production and direct seeding varies with method.
A working definition of planting stock quality was accepted at the 1979 IUFRO Workshop on Techniques for Evaluating Planting Stock Quality in New Zealand: “The quality of planting stock is the degree to which that stock realizes the objectives of management (to the end of the rotation or achievement of specified sought benefits) at minimum cost. Quality is fitness for purpose” (Willen and Sutton 1980). Clear expression of objectives is therefore prerequisite to any determination of planting stock quality (Sutton 1982). Not only does performance have to be determined, but performance has to be rated against the objectives of management (Sutton 1987). Planting stock is produced in order to give effect to the forest policy of the organization.
A distinction needs to be made between “planting stock quality” and “planting stock performance potential” (PSPP). The actual performance of any given batch of outplanted planting stock is determined only in part by the kind and condition, i.e., the intrinsic PSPP, of the planting stock.
The PSPP is impossible to estimate reliably by eye because outward appearance, especially of stock withdrawn from refrigerated storage, can deceive even experienced foresters, who would be offended if their ability were questioned to recognize good planting stock when they saw it. Prior to Wakeley’s (1954) demonstration of the importance of the physiological state of planting stock in determining the ability of the stock to perform after outplanting, and to a considerable extent even afterwards, morphological appearance has generally served as the basis for estimating the quality of planting stock. Gradually, however, a realization developed that more was involved. Tucker et al. (1968), for instance, after assessing 10-year survival data from several experimental white spruce plantations in Manitoba noted that “Perhaps the most important point revealed here is that certain lots of transplants performed better than others”, even though all transplants were handled and planted with care. The intuitive “stock that looks good must be good” is a persuasive, but potentially dangerous maxim. That greatest of teachers, Bitter Experience, has often enough demonstrated the fallibility of such assessment, even though the corollary “stock that looks bad must be bad” is likely to be well founded. The physiological qualities of planting stock are hidden from the eye and must be revealed by testing. The potential for survival and growth of a batch of planting stock may be estimated from various features, morphological and physiological, of the stock or a sample thereof.
The size and shape and general appearance of a seedling can nevertheless give useful indications of PSPP. In low-stress outplanting situations, and with a minimized handling and lifting-planting cycle, a system based on specification for nursery stock and minimum morphological standards for acceptable seedlings works tolerably well (Sutton 1979). In certain circumstances, benefits often accrue from the use of large planting stock of highly ranked morphological grades. Length of leading shoot, diameter of stem, volume of root system, shoot:root ratios, and height:diameter ratios have been correlated with performance under specific site and planting conditions (Mullin and Christl 1981). However, the concept that larger is better negates the underlying complexities. Schmidt-Vogt (1980), for instance, found that whereas mortality among large outplants is greater than among small in the year of planting, mortality in subsequent growing seasons is higher among small outplants than among large. Much of the literature on comparative seedling performance is clouded by uncertainty as to whether the stocks being compared share the same physiological condition; differences invalidate such comparisons (van den Driessche 1976).
Height and root-collar diameter are generally accepted as the most useful morphological criteria (Navratil et al. 1986) and are often the only ones used in specifying standards.Quantification of root system morphology is difficult but can be done, e.g. by using the photometric rhizometer to determine intercept area (Morrison and Armson 1968), or volume by displacement or gravimetric methods (Burdett 1979).
Planting stock is always subject to a variety of conditions that are never optimal in toto. The effect of sub-optimal conditions is to induce stress in the plants. The nursery manager aims, and is normally able to avoid stresses greater than moderate, i.e., restricting stresses to levels that can be tolerated by the plants without incurring serious damage. The adoption of nursery regimes to equip planting stock with characteristics conferring increased ability to withstand outplanting stresses, by managing stress levels in the nursery to “condition” planting stock to increase tolerance to various post-planting environmental stresses, has become widespread, particularly with containerized stock.
Outplanted stock that is unable to tolerate high temperatures occurring at soil surfaces will fail to establish on many forest sites, even in the far north (Helgerson 1990). Factors affecting heat tolerance were investigated by Colombo et al. (1995); the production and roles of heat shock proteins (HSPs) are important in this regard. HSPs, present constitutively in black spruce and many other, perhaps most, higher plants (Key et al. 1981, Kimpel and Key 1985a,b, Colombo et al. 1995) are important both for normal cell functioning and in a stress response mechanism following exposure to high, non-lethal temperature. In black spruce at least, there is an association between HSPs and increased levels of heat tolerance (Coclough 1991, Colombo et al. 1992). Investigation of the diurnal variability in heat tolerance of roots and shoots in black spruce seedlings 14 to 16 weeks old found in all 4 trials that shoot heat tolerance was significantly greater in the afternoon than in the morning (Colombo et al. 1995). The trend in root heat tolerance was similar to that found in the shoots; root systems exposed to 47 °C for 15 minutes in the afternoon averaged 75 new roots after a 2-week growth period, whereas only 28 new roots developed in root systems similarly exposed in the morning. HSP73 was detected in black spruce nuclear, mitochondrial, microsomal, and soluble protein fractions, while HSP72 was observed only in the soluble protein fraction. Seedlings exhibited constitutive synthesis of HSP73 at 26 °C in all except the nuclear membrane fraction in the morning; HSP levels at 26 °C in the afternoon were higher than in the morning in the mitochondrial and microsomal protein factions. Heat shock affected the abundance of HSPs depending on protein fraction and time of day. Without heat shock, nuclear membrane-bound HSP73 was absent from plants in the morning and only weakly present in the afternoon, and heat shock increased the abundance of nuclear membrane. Heat shock also affected the abundance of HSP73 in the afternoon, and caused HSP73 to appear in the morning. In the mitochondrial and microsomal protein fractions, an afternoon heat shock reduced HSP73, whereas a morning heat shock increased HSP73 in the mitochondrial but decreased it in the microsomal fraction. Heat shock increased soluble HSP72/73 levels in both the morning and afternoon. In all instances, shoot and root heat tolerances were significantly greater in the afternoon than in the morning.
Planting stock continues to respire during storage even if frozen (Navratil 1982). Temperature is the major factor controlling the rate, and care must be taken to avoid overheating. Navratil (1982) found that closed containers in cold storage averaged internal temperatures 1.5 °C to 2.0 °C above the nominal storage temperature. Depletion of reserves can be estimated from the decrease in dry weight. Cold-stored 3+0 white spruce nursery stock in northern Ontario had lost 9% to 16% of dry weight after 40 days of storage (Navratil 1982). Carbohydrates can also be determined directly.
The propensity of a root system to develop new roots or extend existing roots cannot be determined by eye, yet it is the factor that makes or breaks the outcome of an outplanting operation. The post-planting development of roots or root systems of coniferous planting stock is determined by many factors, some physiological, some environmental (Sutton 1990). Unsatisfactory rates of post-planting survival unrelated to the morphology of the stock, led to attempts to test the physiological condition of planting stock, particularly to quantify the propensity to produce new root growth. New root growth can be assumed to be necessary for successful establishment of stock after planting, but although the thesis that RGC is positively related to field performance would seem to be reasonable, supporting evidence has been meager.
The physiological condition of seedlings is reflected by changes in root activity. This is helpful in determining the readiness of stock for lifting and storing and also for outplanting after storage. Navratil (1982) reported a virtually perfect (R² = 0.99) linear relationship in the frequency of 3+0 white spruce white root tips longer than 10 mm with time in the fall at Pine Ridge Forest Nursery, Alberta, decreasing during a 3-week period to zero on October 13 in 1982.Root regenerating research with white spruce in Canada (Hambly 1973, Day and MacGillivray 1975, Day and Breunig 1997) followed similar lines to that of Stone’s (1955) pioneering work in California.
Simpson and Ritchie (1997) debated the proposition that root growth potential of planting stock predicts field performance; their conclusion was that root growth potential, as a surrogate for seedling vigor, can predict field performance, but only under such situations as site conditions permit. Survival after planting is only partly a function of an outplant’s ability to initiate roots in test conditions; root growth capacity is not the sole predictor of plantation performance (Scagel and Linderman 2001).
Some major problems militate against greater use of RGC in forestry, including: unstandardized techniques; unstandardized quantification; uncertain correlation between quantified RGC and field performance; variability within given, nominally identical, kinds of planting stock; and the irrelevance of RGC test values determined on a sub-sample of a parent population that subsequently, before it is planted, undergoes any substantive physiological or physical change. In its present form, RGC testing is silviculturally useful chiefly as a means of detecting planting stock that, while visually unimpaired, is moribund (Sutton 1990).
Seedling moisture content can be increased or decreased in storage, depending on various factors including especially the type of container and the kind and amount of moisture-retaining material present. When seedlings exceed 20 bars PMS in storage, survival after outplanting becomes problematical. The Relative Moisture Content of stock lifted during dry conditions can be increased gradually when stored in appropriate conditions. White spruce (3+0) packed in Kraft bags in northern Ontario increased RMC by 20% to 36% within 40 days (Navratil 1982).
Bareroot 1.5+1.5 white spruce were taken from cold storage and planted early in May on a clear-felled boreal forest site in northeastern Ontario (Grossnickle 1988). Similar plants were potted and kept in a greenhouse. In outplanted trees, maximum stomatal conductances (g) were initially low (<0.01 cm/s), and initial base xylem pressure potentials (PSIb) were -2.0 MPa. During the growing season, g increased to about 0.20 cm/s and PSIb to -1.0 MPa. Minimum xylem pressure potential (PSIm) was initially -2.5 MPa, increasing to -2.0 MPa on day 40, and about -1.6 MPa by day 110. During the first half of the growing season, PSIm was below turgor loss point. The osmotic potential at turgor loss point decreased after planting to -2.3 MPa 28 days later. In the greenhouse, minimum values of PSIT were -2.5 MPa (in the first day after planting. the maximum bulk modulus of elasticity was greater in white spruce than in similarly treated jack pine and showed greater seasonal changes. Relative water content (RWC) at turgor loss was 80-87%. Available turgor (TA), defined as the integral of turgor over the range of RWC between PSIb and xylem pressure potential at the turgor loss point) was 4.0% for white spruce at the beginning of the season compared with 7.9% for jack pine, but for the rest of the season TA for jack pine was only 2%, to 3% that of white spruce. Diurnal turgor (Td), the integral of turgor over the range of RWC between PSIb and PSIm, as a percentage of TA was higher in field-planted white spruce than jack pine until the end of the season.
The stomata of both white and black spruce were more sensitive to atmospheric evaporative demands and plant moisture stress during the first growing season after outplanting on 2 boreal sites in northern Ontario than were jack pine stomata (Grossnickle and Blake 1986), physiological differences that favoured growth and establishment being more in jack pine than in the spruces.
With black spruce and jack pine, but not with white spruce, Grossnickle and Blake’s (1987) findings warrant mention in relation to the bareroot-containerized debate. During the first growing season after outplanting, containerized seedlings of both species had greater needle conductance than bareroot seedlings over a range of absolute humidity deficits. Needle conductance of containerized seedlings of both species remained high during periods of high absolute humidity deficits and increasing plant moisture stress. Bareroot outplants of both species had a greater early season resistance to water-flow through the soil–plant–atmosphere continuum (SPAC) than had containerized outplants. Resistance to water flow through the SPAC decreased in bareroot stock of both species as the season progressed, and was comparable to containerized seedlings 9 to 14 weeks after planting. Bareroot black spruce had greater new-root development than containerized stock throughout the growing season.
The greater efficiency of water use in newly transplanted 3-year-old white spruce seedlings under low levels of absolute humidity difference in water-stressed plants immediately after planting (Marsden et al. 1996) helps explain the commonly observed favourable response of young outplants to the nursing effect of a partial canopy. Silvicultural treatments promoting higher humidity levels at the planting microsite should improve white spruce seedling photosynthesis immediately after planting (Marsden et al. 1996).
Stock types (Seedling nomenclature)
Planting stock is grown under many diverse nursery culture regimes, in facilities ranging from sophisticated computerized greenhouses to open compounds. Types of stock include bareroot seedlings and transplants, and various kinds of containerized stock. For simplicity, both container-grown and bareroot stock are generally referred to as seedlings, and transplants are nursery stock that have been lifted and transplanted into another nursery bed, usually at wider spacing. The size and physiological character of stock vary with the length of growing period and with growing conditions. Until the technology of raising containerized nursery stock bourgeoned in the second half of the twentieth- century, bareroot planting stock classified by its age in years was the norm.
Classification by age
The number of years spent in the nursery seedbed by any particular lot of planting stock is indicated by the 1st of a series of numbers. The 2nd number indicates the years subsequently spent in the transplant line, and a zero is shown if indeed there has been no transplanting. A 3rd number, if any, would indicate the years subsequently spent after a second lifting and transplanting. The numbers are sometimes separated by dashes, but separation by plus sign is more logical inasmuch as the sum of the individual numbers gives the age of the planting stock. Thus 2+0 is 2-year-old seedling planting stock that has not been transplanted, and Candy’s (1929) white spruce 2+2+3 stock had spent 2 years in the seedbed, 2 years in transplant lines, and another 3 years in transplant lines after a second transplanting. Variations have included such self-explanatory combinations, such as 1½+1½, etc.
The class of planting stock to use on a particular site is generally selected on the basis of historical record of survival, growth, and total cost of surviving trees (Korstian and Baker 1925). In the Lake States, Kittredge (1929) concluded that good stock of 2+1 white spruce was the smallest size likely to succeed and was better than larger and more expensive stock when judged by final cost of surviving trees.
Classification by seedling description code
Because age alone is an inadequate descriptor of planting stock, various codes have been developed to describe such components of stock characteristics as height, stem diameter, and shoot:root ratio (e.g., Cleary et al. 1978). A description code may include an indication of the intended planting season.
Neither age classification nor seedling description code indicate the physiological condition of planting stock, though rigid adherence to a given cultural regime together with observation of performance over a number of years of planting can produce stock suitable for performing on a “same again” basis.
Classification by system
Planting stock is raised under a variety of systems, but these have devolved generally into 2 main groupings: bareroot and containerized. Manuals specifically for the production of bareroot (Duryea and Landis 1984) and containerized (Tinus and McDonald 1979) nursery stock are valuable resources for the nursery manager. As well, a lot of good information about nursery stock specific to regional jurisdictions is well presented by Cleary et al. (1978) for Oregon, Lavender et al. (1990) for British Columbia, and Wagner and Colombo (2001) for Ontario.
Forest tree plantations
Plantation establishment criteria
Plantations may be considered successful when outplant performance satisfies certain criteria. The term “free growing” is applied in some jurisdictions. Ontario’s “Free-to-Grow” (FTG) equivalent relates to a forest stand that meets a minimum stocking standard and height requirement, and is essentially free of competition from surrounding vegetation that might impede growth (Ontario Class Environmental Assessment for Timber Management 1989). The FTG concept was introduced with the advent of the Forest Management Agreement program in Ontario in 1980 and became applicable to all management units in 1986. Policy, procedures, and methodologies readily applicable by forest unit managers to assess the effectiveness of regeneration programs were still under development during the Class Environmental Assessment hearings.
In British Columbia, the Forest Practices Code (1995) governs performance criteria. To minimize the subjectivity of assessing deciduous competition as to whether or not a plantation is established, minimum specifications of number, health, height, and competition have been specified in British Columbia. However, minimum specifications are still subjectively set and may need to be fine-tuned in order to avoid unwarranted delay in according established status to a plantation. For example, a vigorous white spruce with a strong, multi-budded leading shoot and its crown fully exposed to light on 3 sides would not qualify as free-growing in the current British Columbia Code but would hardly warrant description as unestablished.
Competition arises when individual organisms are sufficiently close together to incur growth constraint through mutual modification of the local environment (Milthorpe 1961). Plants may compete for light, moisture and nutrients, but seldom for space per se. Vegetation management directs more of the site’s resources into usable forest products, rather than just eliminating all competing plants (Buse and Baker 1991). Ideally, site preparation ameliorates competition to levels that relieve the outplant of constraints severe enough to cause prolonged check.
The diversity of boreal and sub-boreal broadleaf-conifer mixed tree species stands, commonly referred to as the “mixedwoods”, largely preclude the utility of generalizations and call for the development of management practices incorporating the greater inherent complexity of broadleaf-conifer mixtures, relative to single-species or mixed-species conifer forest (Simard 1996). After harvesting or other disturbance, mixedwood stands commonly enter a prolonged period in which hardwoods overtop the coniferous component, subjecting them to intense competition in an understorey. It is well established that the regeneration and growth potential of understorey conifers in mixedwood stands is correlated to the density of competing hardwoods (Green 2004). To help apply “free-to-grow” regulations in British Columbia and Alberta, management guidelines based on distance-dependent relations within a limited radius of crop trees were developed, but Lieffers et al. (2002) found that free-growing stocking standards did not adequately characterize light competition between broadleaf and conifer components in boreal mixedwood stands, and further noted that adequate sampling using current approaches would be operationally prohibitive.
Many promising plantations have failed through lack of tending. Young crop trees are often ill-equipped to fight it out with competition resurgent following initial site preparation and planting.
Perhaps the most direct evaluation of the effect of competition on plantation establishment is provided by an effective herbicide treatment. The fact that herbicide treatment does not always produce positive results should not obscure the demonstrated potential of herbicides for significantly promoting plantation establishment. Factors that can vitiate the effectiveness of a herbicide treatment include: weather, especially temperature, prior to and during application; weather, especially wind, during application; weather, especially precipitation, in the 12 to 24 hours after application; vegetation characteristics, including species, size, shape, phenological stage, vigour, and distribution of weeds; crop characteristics, including species, phenology, and condition; the effects of other treatments, such as preliminary shearblading, burning or other prescribed or accidental site preparation; and the herbicide used, including dosage, formulation, carrier, spreader, and mode of application. There is a lot that can go wrong, but a herbicide treatment can be as good or better than any other method of site preparation.
The study of competition dynamics requires both a measure of the competition level and a measure of crop response. Various competition indices have been developed, e.g., by Bella (1971) and Hegyi (1974) based on stem diameter, by Arney (1972), Ek and Monserud (1974), and Howard and Newton (1984) based on canopy development, and Daniels (1976), Wagner (1982), and Weiner (1984) with proximity-based models. Studies generally considered tree response to competition in terms of absolute height or basal area, but Zedaker (1982) and Brand (1986) sought to quantify crop tree size and environmental influences by using relative growth measures.
Tending is the term applied to pre-harvest silvicultural treatment of forest crop trees at any stage after initial planting or seeding. The treatment can be of the crop itself (e.g., spacing, pruning, thinning, and improvement cutting) or of competing vegetation (e.g., weeding, cleaning) (Ford-Robertson 1971).
How many trees per unit area (spacing) that should be planted is not an easily answered question. Establishment density targets or regeneration standards have commonly been based on traditional practice, with the implicit aim of getting the stand quickly to the free-to-grow stage (Willcocks and Bell 1995). Money is wasted if more trees are planted than are needed to achieve desired stocking rates, and the chance to establish other plantations is proportionately diminished. Ingress (natural regeneration) on a site is difficult to predict and often becomes surprisingly evident only some years after planting has been carried out. Early stand development after harvesting or other disturbance undoubtedly varies greatly among sites, each of which has its own peculiar characteristics.
For all practical purposes, the total volume produced by a stand on a given site is constant and optimum for a wide range of density or stocking. It can be decreased, but not increased, by altering the amount of growing stock to levels outside this range (Smith 1962). Initial density affects stand development in that close spacing leads to full site utilization more quickly than wider spacing (OMNR 1989). Economic operability can be advanced by wide spacing even if total production is less than in closely spaced stands.
Beyond the establishment stage, the relationship of average tree size and stand density is very important (Willcocks and Bell 1995). Various density-management diagrams conceptualizing the density-driven stand dynamics have been developed (cf. Drew and Flewelling 1979, Archibald and Bowling 1995). Smith and Brand’s (1988) diagram has mean tree volume on the vertical axis and the number of trees/ha on the horizontal axis: a stand can either have many little trees or a few big ones. The self-thinning line shows the largest number of trees of a given size/ha that can be carried at any given time. However, Willcocks and Bell (1995) caution against using such diagrams unless specific knowledge of the stand trajectory is known.
In the Lake States, plantations have been made with the spacing between trees varying from 3 by 3 to 10 by 10 feet (0.9 m by 0.9 m to 3.0 m by 3.0 m) (Kittredge 1929). Kittredge recommended that no fewer than 600 established trees per acre (1483/ha) be present during the early life of a plantation. To insure this, at least 800 trees per acre (1077/ha) should be planted where 85% survival may be expected, and at least 1200/ac (2970/ha) if only half of them can be expected to live (Toumey and Korstian 1954). This translates into recommended spacings of 5 by 5 to 8 by 8 feet (1.5 m by 1.5 m to 2.4 m by 2.4 m) for plantings of conifers, including white spruce in the Lake States.
A strategy for enhancing natural forests' economic value is to increase their concentration of economically important, indigenous tree species by planting seeds or seedlings for future harvest, which can be accomplished with enrichment planting (EP). This means increasing the planting density (i.e., the numbers of plants per hectare) in an already growing forest stand."
- Weeding: A process of getting rid of samplings' or seedlings' competition by mowing, application of herbicide, or other method of removal from the surroundings.
- Cleaning: Release of select saplings from competition by overtopping trees of a comparable age. The treatment favors trees of a desired species and stem quality.
- Liberation Cutting: A treatment that releases tree seedling or saplings by removing older overtopping trees.
Over-crowded regeneration tends to stagnate. The problem is aggravated in species that have little self-pruning ability, such as white spruce. Spacing is a thinning (of natural regeneration), in which all trees other than those selected for retention at fixed intervals are cut. The term juvenile spacing is used when most or all of the cut trees are unmerchantable (Lloyd 1991). Spacing can be used to obtain any of a wide range of forest management objectives, but it is especially undertaken to reduce density and control stocking in young stands and prevent stagnation, and to shorten the rotation, i.e., to speed the production of trees of a given size. Volume growth of individual trees and the merchantable growth of stands are increased (Hermelin 1991). The primary rationale for spacing is that thinning is the projected decline in maximum allowable cut (Nicks 1991). And since wood will be concentrated on fewer, larger, and more uniform stems, operating and milling costs will be minimized.
Methods for spacing may be: manual, using various tools, including power saws, brush saws, and clippers; mechanical, using choppersand mulchers; chemical; or combinations of several methods. One treatment has had notable success in spacing massively overstocked (<100 000 stems/ha) natural regeneration of spruce and fir in Maine. Fitted to helicopter, the Thru-Valve boom emits herbicide spray droplets 1000 µm to 2000 µm in diameter (MacKay 1991) at very low pressure. Swaths 1.2 m wide and leave strips 2.4 m wide were obtained with “knife-edge” precision when the herbicide was applied by helicopter flying at a height of 21 m at a speed of 40–48 km/h. It seems likely that no other method could be as cost-effective.
A spacing study of 3 conifers (white spruce, red pine and jack pine) was established at Moodie, Manitoba, on flat, sandy, nutritionally poor soils with a fresh moisture regime (Bella 1986). Twenty years after planting, red pine had the largest average dbh, 15% greater than jack pine, while white spruce dbh was less than half that of the pines. Crown width showed a gradual increase with spacing for all 3 conifers. Results to date were suggesting optimum spacings between 1.8 m and 2.4 m for both pines; white spruce was not recommended for planting on such sites.
Comparable data are generated by espacement trials, in which trees are planted at a range of densities. Spacings of 1.25 m, 1.50 m, 1.75 m, 2.00 m, 2.50 m, and 3.00 m on 4 site classes were used in the 1922 trial at Petawawa, Ontario. In the first of 34 old field white spruce plantations used to investigate stand development in relation to spacing at Petawawa, Ontario, regular rows were planted at average spacings of from 4 × 4 to 7 × 7 feet (1.22 m × 1.22 m to 2.13 m × 2.13 m) (Stiell and Berry 1973). Spacings up to 10 × 10 feet (3.05 m × 3.03 m) were subsequently included in the study. Yield tables based on 50 years of data showed:
- a) Except for merchantable volumes at age 20 and site classes 50 and 60, closer spacings gave greater standing volumes at all ages than did wider spacings, the relative difference decreasing with age.
- b) Merchantable volume as a proportion of total volume increases with age, and is greater at wider than at closer spacings.
- c) Current annual volume increment culminates sooner at closer than at wider spacings.
A smaller espacement trial, begun in 1951 near Thunder Bay, Ontario, included white spruce at spacings of 1.8 m, 2.7 m, and 3.6 m (Ontario Ministry of Natural Resources 1989). At the closest spacing, mortality had begun at 37 years, but not at the wider spacings.
The oldest interior spruce espacement trial in British Columbia was established in 1959 near Houston in the Prince Rupert Forest Region (Pollack et al. 1992). Spacings of 1.2 m, 2.7 m, 3.7 m, and 4.9 m were used, and trees were measured 6, 12, 16, 26, and 30 years after planting. At wide espacements, trees developed larger diameters, crowns, and branches, but (at 30 years) basal area and total volume/ha were greatest in the closest espacement (Table 6.38). In more recent trials in the Prince George Region of British Columbia (Table 6.39) and in Manitoba (Bella and De Franceschi 1980), planting density of white spruce had no effect on growth after up to 16 growing seasons, even at spacings as low as 1.2 m. The slowness of juvenile growth and of crown closure delay the response to intra-competition. Initially, close spacing might even provide a positive nurse effect to offset any negative response to competition.
Thinning is an operation that artiﬁcially reduces the number of trees growing in a stand with the aim of hastening the development of the remainder. The goal of thinning is to control the amount and distribution of available growing space. By altering stand density, foresters can influence the growth, quality, and health of residual trees. It also provides an opportunity to capture mortality and cull the commercially less desirable, usually smaller and malformed, trees. Unlike regeneration treatments, thinnings are not intended to establish a new tree crop or create permanent canopy openings.
Thinning greatly influences the ecology and micro-meteorology of the stand, lowering the inter-tree competition for water. The removal of any tree from a stand has repercussions on the remaining trees both above-ground and below. Silvicultural thinning is a powerful tool that can be used to influence stand development, stand stability, and the characteristics of the harvestable products.
When considering intensive conifer plantations designed for maximum production, it is essential to remember that tending and thinning regimes and wind and snow damage are intimately related (Navratil et al. 1991).
Common thinning methods:
- Low Thinning: method of what they do is what they predicted to happen naturally. It emphasizes crown class.
- Crown Thinning (thinning from above or French method)
- Selection Thinning (thinning of dominants or Borggreve method). It focuses primarily on quality.
- Mechanical Thinning (row thinning or geometric thinning)
- Free Thinning
- Loose Thinning
Previous studies have demonstrated that repeated thinnings over the course of a forest rotation increase carbon stores relative to stands that are clear-cut on short rotations and that the carbon benefits differ according to thinning method (e.g., thinning from above versus below).
Ecological thinning is where the primary aim of forest thinning is to increase growth of selected trees, favoring development of wildlife habitat (such as hollows) rather than focusing on increased timber yields. Ecological thinning can be considered a new approach to landscape restoration for some types of eucalypt forests and woodlands in Australia.
When natural regeneration or artificial seeding has resulted in dense, overstocked young stands, natural thinning will in most cases eventually reduce stocking to more silviculturally desirable levels. But by the time some trees reach merchantable size, others will be overmature and defective, and others will still be unmerchantable. The yield of merchantable wood can be greatly increased and the rotation shortened by precommercial thinning (Day 1967). Mechanical and chemical methods have been applied, but their costliness has militated against their ready adoption.
Pruning, as a silvicultural practice, refers to the removal of the lower branches of the young trees (also giving the shape to the tree) so clear knot-free wood can subsequently grow over the branch stubs. Clear knot-free lumber has a higher value. Pruning has been extensively carried out in the Radiata pine plantations of New Zealand and Chile, however the development of Finger joint technology in the production of lumber and mouldings has led to many forestry companies reconsidering their pruning practices. "Brashing" is an alternative name for the same process. Pruning can be done to all trees, or more cost effectively to a limited number of trees. There are two types of pruning: natural or self-pruning and artificial pruning. Most cases of self-pruning happen when branches do not receive enough sunlight and die. Wind can also take part in natural pruning which can break branches. Artificial pruning is where people are paid to come and cut the branches. Or it can be natural, where trees are planted close enough that the effect is to cause self-pruning of low branches as energy is put into growing up for light reasons and not branchiness.
The term stand conversion refers to a change from one silvicultural system to another and includes species conversion, i.e., a change from one species (or set of species) to another (Ford-Robertson 1971). Such change can be effected intentionally by various silvicultural means, or incidentally by default e.g., when high-grading has removed the coniferous content from a mixedwood stand, which then becomes exclusively self-perpetuating aspen. In general, such sites as these are the most likely to be considered for conversion.
Growth and yield
In discussing yields that might be expected from the Canadian spruce forests, Haddock (1961) noted that Wright’s (1959) quotation of spruce yields in the British Isles of 220 cubic feet per acre (15.4 m3/ha) per year and in Germany of 175 cubic feet per acre (12.25 m3/ha) per year was misleading, at least if it was meant to imply that such yields might be approached in the Boreal Forest Region of Canada. Haddock thought that Wright’s suggestion of 20 to 40 (average 30) cubic feet per acre (1.4 m3/ha to 2.8 m3/ha (average 2.1 m3/ha) per year was more reasonable, but still somewhat optimistic.
The principal way forest resource managers influence growth and yield is to manipulate the mixture of species and number (density) and distribution (stocking) of individuals that form the canopy of the stand (Davis and Johnson 1987, Burgess et al. 2001). Species composition of much of the boreal forest in North America already differs greatly from its pre-exploitation state. There is less spruce and more hardwoods in the second-growth forest than in the original forest; Hearnden et al. (1996) calculated that the spruce cover type had declined from 18% to only 4% of the total forested area in Ontario. Mixedwood occupies a greater proportion of Ontario’s second-growth forest (41%) than in the original (36%), but its component of white spruce is certainly much diminished.
Growth performance is certainly influenced by site conditions and thus by the kind and degree of site preparation in relation to the nature of the site. It is important to avoid the assumption that site preparation of a particular designation will have a particular silvicultural outcome. Scarification, for instance, not only covers a wide range of operations that scarify, but also any given way of scarifying can have significantly different results depending on site conditions at the time of treatment. In point of fact, the term is commonly misapplied. Scarification is defined (Ford-Robertson 1971) as “Loosening the top soil of open areas, or breaking up the forest floor, in preparation for regenerating by direct seeding or natural seedfall”, but the term is often misapplied to practices that include scalping, screefing, and blading, which pare off low and surface vegetation, together with most off its roots to expose a weed-free surface, generally in preparation for sowing or planting thereon.
Thus, it is not surprising that literature can be used to support the view that the growth of seedlings on scarified sites is much superior to that of growth on similar sites that have not been scarified (cf. Waldron 1966, Butt et al. 1989, Youngblood and Zasada 1991), while other evidence supports the contrary view that scarification can reduce growth (cf. Day 1970, Herring and McMinn 1980, McMinn 1986). Detrimental results can be expected from scarification that impoverishes the rooting zone or exacerbates edaphic or climatic constraints.
Burning site preparation has enhanced spruce seedling growth (Butt et al. 1989), but it must be supposed that burning could be detrimental if the nutrient capital is significantly depleted.
|Percent cover (%)||Vegetation Description|
|Below 1||No vegetation|
|1-3||Moss carpet with a few fir seedlings|
|4-10||Herbaceous plants appear|
|10-25||Bramble, herbs, fairly vigorous spruce seedlings|
|>25||Herbs, brambles very dense, vigorous, no moss|
A factor of some importance in solar radiation–reproduction relationships is excess heating of the soil surface by radiation (Reifsnyder and Lull 1965). This is especially important for seedlings, such as spruce, whose first leaves do not shade the base of the stem at the soil surface. Surface temperatures in sandy soils on occasion reach lethal temperatures of 50 °C to 60 °C.
Common methods of harvesting
Silvicultural regeneration methods combine both the harvest of the timber on the stand and re-establishment of the forest. The proper practice of sustainable forestry should mitigate the potential negative impacts, but all harvest methods will have some impacts on the land and residual stand. The practice of sustainable forestry limits the impacts such that the values of the forest are maintained in perpetuity. Silvicultural prescriptions are specific solutions to a specific set of circumstances and management objectives. Following are some common methods:
Conventional clearcut harvesting is relatively simple: all trees on a cutblock are felled and bunched with bunches aligned to the skidding direction, and a skidder then drags the bunches to the closest log deck (Sauder 1996). Feller-buncher operators concentrate on the width of the felled swath, the number of trees in a bunch, and the alignment of the bunch. Providing a perimeter boundary is felled during daylight, night-shift operations can continue without the danger of trespassing beyond the block. Productivity of equipment is maximized because units can work independently of one another.
An even-aged regeneration method that can employ either natural or artificial regeneration. It involves the complete removal of the forest stand at one time. Clearcutting can be biologically appropriate with species that typically regenerate from stand replacing fires or other major disturbances, such as Lodgepole Pine (Pinus contorta). Alternatively, clearcutting can change the dominating species on a stand with the introduction of non-native and invasive species as was shown at the Blodgett Experimental Forest near Georgetown California. Additionally, clearcutting can prolong slash decomposition, expose soil to erosion, impact visual appeal of a landscape and remove essential wildlife habitat. It is particularly useful in regeneration of tree species such as Douglas-fir (Pseudotsuga menziesii) which is shade intolerant.[verification needed]. In addition, the general public's distaste for even-aged silviculture, particularly clearcutting, is likely to result in a greater role for uneven-aged management on public lands as well. Across Europe, and in parts of North America, even-aged, production-orientated and intensively managed plantations are beginning to be regarded in the same way as old industrial complexes: something to abolish or convert to something else.
Clearcutting will impact many site factors important in their effect on regeneration, including air and soil temperatures. Kubin and Kemppainen (1991), for instance, measured temperatures in northern Finland from 1974 through 1985 in 3 clear-felled areas and in 3 neighouring forest stands dominated by Norway spruce. Clear felling had no significant influence on air temperature at 2 m above the ground surface, but the daily air temperature maxima at 10 cm were greater in the clear-felled area than in the uncut forest, while the daily minima at 10 cm were lower. Night frosts were more common in the clear-felled area. Daily soil temperatures at 5 cm depth were 2 °C to 3 °C greater in the clear-felled area than in the uncut forest, and temperatures at depths of 50 cm and 100 cm were 3 °C to 5 °C greater. The differences between the clear-felled and uncut areas did not diminish during the 12 years following cutting.
A regeneration method which depends on the sprouting of cut trees. Most hardwoods, the coast redwood, and certain pines naturally sprout from stumps and can be managed through coppicing. Coppicing is generally used to produce fuelwood, pulpwood, and other products dependent on small trees. A close relative of coppicing is pollarding. Three systems of coppice woodland management are generally recognized: simple coppice, coppice with standards, and the coppice selection system.
- In Compound coppicing or coppicing with standards, some of the highest quality trees are retained for multiple rotations in order to obtain larger trees for different purposes.
Prochnau (1963), 4 years after sowing, found that 14% of viable white spruce seed sown on mineral soil had produced surviving seedlings, at a seed:seedling ratio of 7.1:1. With Engelmann spruce, Smith and Clark (1960) obtained average 7th year seed:seedling ratios of 21:1 on scarified seedbeds on dry sites, 38:1 on moist sites, and 111:1 on litter seedbeds.
The group selection method is an uneven-aged regeneration method that can be used when mid-tolerant species regeneration is desired. The group selection method can still result in residual stand damage in dense stands, however directional falling can minimize the damage. Additionally, foresters can select across the range of diameter classes in the stand and maintain a mosaic of age and diameter classes.
Méthode du contrôle
Classical European silviculture achieved impressive results with systems such as Henri Biolley’s méthode du contrôle in Switzerland, in which the number and size of trees harvested were determined by reference to data collected from every tree in every stand measured every 7 years (Biolley 1920).
While not designed to be applied to boreal mixedwoods, the méthode du contrôle is described briefly here to illustrate the degree of sophistication applied by some European foresters to the management of their forests. Development of management techniques that allowed for stand development to be monitored and guided into sustainable paths were in part a response to past experience, particularly in Central European countries, of the negative effects of pure, uniform stands with species often unsuited to the site, which greatly increased the risk of soil degradation and biotic diseases. Increased mortality and decreased increment generated widespread concern, especially after reinforcement by other environmental stresses.
More or less uneven-aged, mixed forests of preponderantly native species, on the other hand, treated along natural lines, have proved to be healthier and more resistant to all kinds of external dangers; and in the long run such stands are more productive and easier to protect.
However, irregular stands of this type are definitely more difficult to manage—new methods and techniques had to be sought particularly for the establishment of inventories, as well as increment control and yield regulation. In Germany, for instance, since the beginning of the nineteenth-century under the influence of G.L. Hartig (1764–1837), yield regulation has been effected almost exclusively by allotment or formula methods based on the conception of the uniform normal forest with a regular succession of cutting areas.
In France, on the other hand, efforts were made to apply another kind of forest management, one that aimed to bring all parts of the forest to a state of highest productive capacity in perpetuity. In 1878, the French forester A. Gurnaud (1825–1898) published a description of a méthode du contrôle for determining increment and yield. The method was based on the fact that through careful, selective harvesting, the productivity of the residual stand can be improved, because timber is removed as a cultural operation. In this method, the increment of stands is accurately determined periodically with the object of gradually converting the forest, through selective management and continuous experimentation, to a condition of equilibrium at maximum productive capacity.
Henri Biolley (1858–1939) was the first to apply Gurnaud's inspired ideas to practical forestry. From 1890 on, he managed the forests of his Swiss district according to these principles, devoting himself for almost 50 years to the study of increment and a treatment of stands directed towards the highest production, and proving the practicability of the check method. In 1920, he published this study giving a theoretical basis of management of forests under the check method, describing the procedures to be applied in practice (which he partly developed and simplified), and evaluating the results.
Biolley's pioneering work formed the basis upon which most Swiss forest management practices were later developed, and his ideas have been generally accepted. Today, with the trend of intensifying forest management and productivity in most countries, the ideas and application of careful, continuous treatment of stands with the aid of the volume check method are meeting with ever-growing interest.
Row and broadcast seeding
Spot and row seeders use less seed that does broadcast ground or aerial seeding but may induce clumping. Row and spot seeding confer greater ability to control seed placement than does broadcast seeding. Also, only a small percentage of the total area needs to be treated.
In the aspen type of the Great Lakes region, direct sowing of the seed of conifers has usually failed (Kittredge and Gervorkiantz 1929). However, Gardner (1980) after trials in Yukon, which included broadcast seeding of white spruce seed at 2.24 kg/ha that secured 66.5% stocking in the Scarified Spring Broadcast treatment 3 years after seeding, concluded that the technique held “considerable promise”.
An even-aged regeneration method that retains widely spaced residual trees in order to provide uniform seed dispersal across a harvested area. In the seed-tree method, 2-12 seed trees per acre (5-30/ha) are left standing in order to regenerate the forest. They will be retained until regeneration has become established at which point they may be removed. It may not always be economically viable or biologically desirable to re-enter the stand to remove the remaining seed trees. Seed-tree cuts can also be viewed as a clearcut with natural regeneration and can also have all of the problems associated with clearcutting. This method is most suited for light-seeded species and those not prone to windthrow.
Selection systems are appropriate where uneven stand structure is desired, particularly where the need to retain continuous forest cover for aesthetic or environmental reasons outweighs other management considerations. Selection logging has been suggested as being of greater utility than shelterwood systems in regenerating old-growth Engelmann Spruce Sub-alpine Fir (ESSF) stands in southern British Columbia (Weetman and Vyse 1990). In most areas, selection logging favours regeneration of fir more than the more light-demanding spruce (Glew 1963, Alexander 1987, Coates et al. 1994). In some areas, selection logging can be expected to favour spruce over less tolerant hardwood species (Zasada 1972) or lodgepole pine (Coates et al. 1994).
Shelter spot seeding
The use of shelters to improve germination and survival in spot seedings seeks to capture the benefits of greenhouse culture, albeit miniature. The Hakmet seed shelter, for instance, is a semi-transparent plastic cone 8 cm high, with openings of 7 cm diameter in the 7.5 cm diameter base and 17 mm diameter in the 24 mm diameter top (Lähde and Tuohisaari 1976). This miniature greenhouse increases air humidity, reduces soil desiccation, and raises air and soil temperatures to levels more favourable to germination and seedling growth than those offered by unprotected conditions. The shelter is designed to break down after a few years of exposure to ultraviolet radiation.
Seed shelters and spring sowing significantly improved stocking compared with bare spot seeding, but sheltering did not significantly improve growth. Stocking of bare seedspots was extremely low, possibly due to smothering of seedlings by abundant broadleaf and herbaceous litter, particularly that from aspen and red raspberry, and exacerbated by strong competition from graminoids and raspberry.
Cone shelters (Cerkon™) usually produced greater survival than unsheltered seeding on scarified seedspots in trials of direct seeding techniques in interior Alaska, and funnel shelters (Cerbel™) usually produced greater survival than unsheltered seeding on non-scarified seedspots (Putman and Zasada 1986). Both shelter types are manufactured by AB Cerbo in Trollhättan, Sweden. Both are made of light-degradable, white, opaque plastic, and are 8 cm high when installed.
White spruce seed was sown in Alaska on a burned site in summer 1984, and protected by white plastic cones on small spots scarified by hand, or by white funnels placed directly into the residual ash and organic material (Putman and Zasada 1985). A group of 6 ravens (Corvus corax) was observed in the area about 1 week after sowing was completed in mid-June. Damage averaged 68% with cones and 50% with funnels on an upland area, and 26% with funnels on a floodplain area. Damage by ravens was only 0.13% on unburned but otherwise similar areas.
In seeding trials in Manitoba between 1960 and 1966 aimed at converting aspen stands to spruce–aspen mixedwoods, 1961 scarification in the Duck Mountain Provincial Forest remained receptive to natural seeding for many years (Dyck 1994).
In general terms, the shelterwood system is a series of partial cuts that removes the trees of an existing stand over several years and eventually culminates in a final cut that creates a new even-aged stand. It is an even-aged regeneration method that removes trees in a series of three harvests: 1) Preparatory cut; 2) Establishment cut; and 3) Removal cut. The success of practising a shelterwood system is closely related to: 1. the length of the regeneration period, i.e. the time from the shelterwood cutting to the date when a new generation of trees has been established; 2.the quality of the new tree stand with respect to stand density and growth; and 3.the value increment of the shelter trees. Information on the establishment, survival and growth of seedlings influenced by the cover of shelter trees, as well as on the growth of these trees, is needed as a basis for modelling the economic return of practising a shelterwood system. The method's objective is to establish new forest reproduction under the shelter of the retained trees. Unlike the seed-tree method, residual trees alter understory environmental conditions (i.e. sunlight, temperature, and moisture) that influence tree seedling growth. This method can also find a middle ground with the light ambiance by having less light accessible to competitors while still being able to provide enough light for tree regeneration. Hence, shelterwood methods are most often chosen for site types characterized by extreme conditions, in order to create a new tree generation within a reasonable time period. These conditions are valid foremost on level ground sites which are either dry and poor or moist and fertile.
Shelterwood systems involve 2, 3, or exceptionally more partial cuttings. A final cut is made once adequate natural regeneration has been obtained. The shelterwood system is most commonly applied as a 2-cut uniform shelterwood, first an initial regeneration (seed) cut, the second a final harvest cut. In stands less than 100 years old, a light preparatory cut can be useful (Zasada 1972). A series of intermediate cuts at intervals of 10–20 years has been recommended for intensively managed stands (Alexander 1987).
From operational or economic standpoints, however, there are disadvantages to the shelterwood system: harvesting costs are higher; trees left for deferred cutting may be damaged during the regeneration cut or related extraction operations; the increased risk of blowdown threatens the seed source; damage from bark beetles is likely to increase; regeneration may be damaged during the final cut and related extraction operations; the difficulty of any site preparation would be increased; and incidental damage to regeneration might be caused by any site preparation operations (Day 1970; Zasada 1972; Alexander 1973, 1987; Baldwin 1977).
The single-tree selection method is an uneven-aged regeneration method most suitable when shade tolerant species regeneration is desired. It is typical for older and diseased trees to be removed, thus thinning the stand and allowing for younger, healthy trees to grow. Single-tree selection can be very difficult to implement in dense or sensitive stands and residual stand damage can occur. This method is also disturbs the canopy layer the least out of all other methods.
Spot seeding was found to be the most economical and reliable of the direct seeding methods for converting aspen and paper birch to spruce and pine (Robertson 1927). In the Chippewa National Forest (Lake States), seed-spot sowing of 10 seeds each of white spruce and white pine under 40-year aspen after different degrees of cutting on gave second-season results clearly indicating the need to remove or disturb the forest floor to obtain germination of seeded white spruce and white pine (Kittredge and Gevorkiantz 1929).
Spot seeding of coniferous seed, including white spruce, has had occasional success, but several constraining factors commonly limit germination success: the drying out of the forest floor before the roots of germinants reach underlying moisture reserves; and, particularly under hardwoods, the smothering of small seedlings by snow-pressed leaf litter and lesser vegetation. Kittredge and Gervorkiantz (1929) determined that removal of the aspen forest floor increased germination percentage after the second season in seed spots of both white pine and white spruce, in 4 plots, from 2.5% to 5%, from 8% to 22%, from 1% to 9.5%, and from 0% to 15%.
Spot seeding requires less seed than broadcast seeding and tends to achieve more uniform spacing, albeit sometimes with clumping. The devices used in Ontario for manual spot seeding are the “oil can” seeder, seeding sticks, and shakers (Scott 1970). The oil can is a container fitted with a long spout through which a predetermined number of seeds are released with each flick of the seeder.
Harvesting cutblocks where only a portion of the trees are to be removed is very different from clearcutting (Sauder 1995). First, trails must be located to provide access for the felling and skidding/forwarding equipment. These trails must be carefully located to ensure that the trees remaining meet the desired quality criteria and stocking density. Second, the equipment must not damage the residual stand. The further desiderata are outlined by Sauder (1995).
The dearth of seed and a deficiency of receptive seedbeds were recognized as major reasons for the lack of success of clearcut harvesting. One remedy attempted in British Columbia and Alberta has been alternate strip cutting (Butt 1988). The greater seed source from uncut trees between the cut strips, and the disturbance to the forest floor within the cut strips could be expected to increase the amount of natural regeneration. Trees were cut to a diameter limit in the cut strips, but large trees in the leave strips often proved too much of a temptation and were cut too (Coates et al. 1994), thus removing those trees that would otherwise have been the major source of seed.
An unfortunate consequence of strip thinning was the build-up of spruce beetle populations. Shaded slash from the initial cut, together with an increase in the number of windthrown trees in the leave strips, provided conditions ideally suited to the beetle (Dyer and Taylor 1968).
DeLong et al. (1991) suggested underplanting 30- to 40-year-old aspen stands, on the basis of the success of natural spruce in regenerating under stands of such stands: “By planting, spacing can be controlled enabling easier protection of the spruce during stand entry for harvesting of the aspen overstorey”.
A harvesting and regeneration method which is a relatively new silvicultural system that retains forest structural elements (stumps, logs, snags, trees, understory spieces and undisturbed layers of forest floor) for at least one rotation in order to preserve environmental values associated with structurally complex forests.
"Uneven-aged and even-aged methods differ in the scale and intensity of disturbance. Uneven-aged methods maintain a mix of tree sizes or ages within a habitat patch by periodically harvesting individual or small groups of trees, Even-aged methods harvest most or all of the overstory and create a fairly uniform habitat patch dominated by trees of the same age". Even-aged management systems have been the prime methods to use when studying the effects on birds.
A survey in 1955–56 to determine survival, development, and the reasons for success or failure of conifer pulpwood plantations (mainly of white spruce) in Ontario and Quebec up to 32 years old found that the bulk of the mortality occurred within the first 4 years of planting, unfavourable site and climate being the main causes of failure (Stiell 1958).
Naturally regenerated trees in an understorey prior to harvesting constitute a classic case of good news and bad news. Understorey white spruce is of particular importance in mixedwoods dominated by aspen, as in the B15, B18a, and B19a Sections of Manitoba (Rowe 1972), and elsewhere. Until the latter part of the last century, white spruce understorey was mostly viewed as money in the bank on a long-term, low interest deposit, with final yield to be realized after slow natural succession (Brace and Bella 1988), but the resource became increasingly threatened with the intensification of harvesting of aspen. White spruce plantations on mixedwood sites proved expensive, risky, and generally unsuccessful (Brace and Bella 1988). This prompted efforts to see what might be done about growing aspen and white spruce on the same landbase by protecting existing white spruce advance growth, leaving a range of viable crop trees during the first cut, then harvesting both hardwoods and spruce in the final cut. Information about the understorey component is critical to spruce management planning. The ability of then current harvesting technology and crews employed to provide adequate protection for white spruce understories was questioned by Brace and Bella. Specialized equipment and training, perhaps with financial incentives, may be needed to develop procedures that would confer the degree of protection needed for the system to be feasible. Effective understorey management planning requires more than improved mixedwood inventory.
Avoidance of damage to the understorey will always be a desideratum. Sauder’s (1990) paper on mixedwood harvesting describes studies designed to evaluate methods of reducing non-trivial damage to understorey residuals that would compromise their chance of becoming a future crop tree. Sauder concluded that: (1) operational measures that protected residual stems may not unduly increase costs, (2) all felling, conifers and hardwoods, needs to be done in one operation to minimize the entry of the feller-buncher into the residual stand, (3) several operational procedures can reduce understorey damage, some of them without incurring extra costs, and (4) successful harvesting of treatment blocks depends primarily on the intelligent location of skid trails and landings. In summary, the key to protecting the white spruce understorey without sacrificing logging efficiency is a combination of good planning, good supervision, the use of appropriate equipment, and having conscientious, well-trained operators.Even the best plan will not reduce understorey damage unless its implementation is supervised (Sauder and Sinclair 1989).
New stands need to be established to provide for future supply of commercial white spruce from 150 000 ha of boreal mixedwoods in 4 of Rowe’s (1972) regional Forest Sections straddling Alberta, Saskatchewan, and Manitoba, roughly from Peace River AB to Brandon MB (Brace 1989). In the 1980s, with harvesting using conventional equipment and procedures, a dramatic increase in the demand for aspen posed a serious problem for the associated spruce understorey. Formerly, white spruce in the understories had developed to commercial size through natural succession under the protection of the hardwoods. Brace articulated a widespread concern: “The need for protection of spruce as a component of boreal mixedwoods goes beyond concern for the future commercial softwood timber supply. Concerns also include fisheries and wildlife habitat, aesthetics and recreation, a general dissatisfaction with cleacutting in mixedwoods and a strong interest in mixedwood perpetuation, as expressed recently in 41 public meetings on forestry development in northern Alberta...” (Brace 1989).
On the basis of tests of 3 logging systems in Alberta, Brace (1990) affirmed that significant amounts of understorey can be retained using any of those systems provided that sufficient effort is directed towards protection. Potential benefits would include increased short-term softwood timber supply, improved wildlife habitat and cutblock aesthetics, as well as reduced public criticism of previous logging practices. Stewart et al. (2001) developed statistical models to predict the natural establishment and height growth of understorey white spruce in the boreal mixedwood forest in Alberta using data from 148 permanent sample plots and supplementary information about height growth of white spruce regeneration and the amount and type of available substrate. A discriminant model correctly classified 73% of the sites as to presence or absence of a white spruce understorey, based on the amount of spruce basal area, rotten wood, ecological nutrient regime, soil clay fraction, and elevation, although it explained only 30% of the variation in the data. On sites with a white spruce understorey, a regression model related the abundance of regeneration to rotten wood cover, spruce basal area, pine basal area, soil clay fraction, and grass cover (R² = 0.36). About half the seedlings surveyed grew on rotten wood, and only 3% on mineral soil, and seedlings were 10 times more likely to have established on these substrates than on litter. Exposed mineral soil covered only 0.3% of the observed transect area.
Advance growth management
Advance growth management, i.e., the use of suppressed understorey trees, can reduce reforestation costs, shorten rotations, avoid denuding the site of trees, and also reduce adverse impacts on aesthetic, wildlife, and watershed values (Johnstone 1978, McCaughey and Schmidt 1982). To be of value, advance growth must have acceptable species composition and distribution, have potential for growth following release, and not be vulnerable to excessive damage from logging.
The age of advance growth is difficult to estimate from its size (Alexander 1958), as white that appears to be 2- to 3-year-old may well be more than 20 years old (Ball and Kolabinski 1979). However, age does not seem to determine the ability of advance growth of spruce to respond to release (Johnstone 1978, McCaughey and Schmidt 1982, McCaughey and Ferguson 1988), and trees older than 100 years have shown rapid rates of growth after release. Nor is there a clear relationship between the size of advance growth and its growth rate when released.
Where advance growth consists of both spruce and fir, the latter is apt to respond to release more quickly than the former, whereas spruce does respond (Stettler 1958, Smith and Wass 1979). If the ratio of fir to spruce is large, however, the greater responsiveness to release of fir may subject the spruce to competition severe enough to negate much of the effect of release treatment. Even temporary relief from shrub competition has increased height growth rates of white spruce in northwestern New Brunswick, enabling the spruce to overtop the shrubs (Baskerville 1961).
Site preparation is any of various treatments applied to a site in order to ready it for seeding or planting. The purpose is to facilitate the regeneration of that site by the chosen method. Site preparation may be designed to achieve, singly or in any combination: improved access, by reducing or rearranging slash, and amelioration of adverse forest floor, soil, vegetation, or other biotic factors. Site preparation is undertaken to ameliorate one or more constraints that would otherwise be likely to thwart the objectives of management. A valuable bibliography on the effects of soil temperature and site preparation on subalpine and boreal tree species has been prepared by McKinnon et al. (2002).
Site preparation is the work that is done before a forest area is regenerated. Some types of site preparation are burning.
Broadcast burning is commonly used to prepare clearcut sites for planting, e.g., in central British Columbia (Macadam 1987), and in the temperate region of North America generally (Kiil and Chrosciewicz 1970).
Prescribed burning is carried out primarily for slash hazard reduction and to improve site conditions for regeneration; all or some of the following benefits may accrue:
- a) Reduction of logging slash, plant competition, and humus prior to direct seeding, planting, scarifying or in anticipation of natural seeding in partially cut stands or in connection with seed-tree systems.
- b) Reduction or elimination of unwanted forest cover prior to planting or seeding, or prior to preliminary scarification thereto.
- c) Reduction of humus on cold, moist sites to favour regeneration.
- d) Reduction or elimination of slash, grass, or brush fuels from strategic areas around forested land to reduce the chances of damage by wildfire.
Prescribed burning for preparing sites for direct seeding was tried on a few occasions in Ontario, but none of the burns was hot enough to produce a seedbed that was adequate without supplementary mechanical site preparation (Scott 1970).
Changes in soil chemical properties associated with burning include significantly increased pH, which Macadam (1987) in the Sub-boreal Spruce Zone of central British Columbia found persisting more than a year after the burn. Average fuel consumption was 20 to 24 t/ha and the forest floor depth was reduced by 28% to 36%. The increases correlated well with the amounts of slash (both total and ≥7 cm diameter) consumed. The change in pH depends on the severity of the burn and the amount consumed; the increase can be as much as 2 units, a 100-fold change (Holt 1955). Deficiencies of copper and iron in the foliage of white spruce on burned clearcuts in central British Columbia might be attributable to elevated pH levels (Ballard 1985).
Even a broadcast slash fire in a clearcut does not give a uniform burn over the whole area. Tarrant (1954), for instance, found only 4% of a 140-ha slash burn had burned severely, 47% had burned lightly, and 49% was unburned. Burning after windrowing obviously accentuates the subsequent heterogeneity.
Marked increases in exchangeable calcium also correlated with the amount of slash at least 7 cm in diameter consumed (Macadam 1987). Phosphorus availability also increased, both in the forest floor and in the 0 cm to 15 cm mineral soil layer, and the increase was still evident, albeit somewhat diminished, 21 months after burning. However, in another study (Taylor and Feller 1987) in the same Sub-boreal Spruce Zone found that although it increased immediately after the burn, phosphorus availability had dropped to below pre-burn levels within 9 months.
Nitrogen will be lost from the site by burning (Little and Klock 1985, Taylor and Feller 1987, Macadam 1987), though concentrations in remaining forest floor were found by Macadam (1987) to have increased in 2 of 6 plots, the others showing decreases. Nutrient losses may be outweighed, at least in the short term, by improved soil microclimate through the reduced thickness of forest floor where low soil temperatures are a limiting factor.
The Picea/Abies forests of the Alberta foothills are often characterized by deep accumulations of organic matter on the soil surface and cold soil temperatures, both of which make reforestation difficult and result in a general deterioration in site productivity; Endean and Johnstone (1974) describe experiments to test prescribed burning as a means of seedbed preparation and site amelioration on representative clear-felled Picea/Abies areas. Results showed that, in general, prescribed burning did not reduce organic layers satisfactorily, nor did it increase soil temperature, on the sites tested. Increases in seedling establishment, survival, and growth on the burned sites were probably the result of slight reductions in the depth of the organic layer, minor increases in soil temperature, and marked improvements in the efficiency of the planting crews. Results also suggested that the process of site deterioration has not been reversed by the burning treatments applied.
Slash weight (the oven-dry weight of the entire crown and that portion of the stem < 4 inches in diameter) and size distribution are major factors influencing the forest fire hazard on harvested sites (Kiil 1965). Forest managers interested in the application of prescribed burning for hazard reduction and silviculture, were shown a method for quantifying the slash load by Kiil (1968). In west-central Alberta, he felled, measured, and weighed 60 white spruce, graphed (a) slash weight per merchantable unit volume against diameter at breast height (dbh), and (b) weight of fine slash (<1.27 cm) also against dbh, and produced a table of slash weight and size distribution on one acre of a hypothetical stand of white spruce. When the diameter distribution of a stand is unknown, an estimate of slash weight and size distribution can be obtained from average stand diameter, number of trees per unit area, and merchantable cubic foot volume. The sample trees in Kiil’s study had full symmetrical crowns. Densely growing trees with short and often irregular crowns would probably be overestimated; open-grown trees with long crowns would probably be underestimated.
The need to provide shade for young outplants of Engelmann spruce in the high Rocky Mountains is emphasized by the U.S. Forest Service. Acceptable planting spots are defined as microsites on the north and east sides of down logs, stumps, or slash, and lying in the shadow cast by such material (Ronco 1975). Where the objectives of management specify more uniform spacing, or higher densities, than obtainable from an existing distribution of shade-providing material, redistribution or importing of such material has been undertaken.
Site preparation on some sites might be done simply to facilitate access by planters, or to improve access and increase the number or distribution of microsites suitable for planting or seeding.
Wang et al. (2000) determined field performance of white and black spruces 8 and 9 years after outplanting on boreal mixedwood sites following site preparation (Donaren disc trenching versus no trenching) in 2 plantation types (open versus sheltered) in southeastern Manitoba. Donaren trenching slightly reduced the mortality of black spruce but significantly increased the mortality of white spruce. Significant difference in height was found between open and sheltered plantations for black spruce but not for white spruce, and root collar diameter in sheltered plantations was significantly larger than in open plantations for black spruce but not for white spruce. Black spruce open plantation had significantly smaller volume (97 cm³) compared with black spruce sheltered (210 cm³), as well as white spruce open (175 cm³) and sheltered (229 cm³) plantations. White spruce open plantations also had smaller volume than white spruce sheltered plantations. For transplant stock, strip plantations had a significantly higher volume (329 cm³) than open plantations (204 cm³). Wang et al. (2000) recommended that sheltered plantation site preparation should be used.
Up to 1970, no “sophisticated” site preparation equipment had become operational in Ontario (J. Hall 1970), but the need for more efficacious and versatile equipment was increasingly recognized. By this time, improvements were being made to equipment originally developed by field staff, and field testing of equipment from other sources was increasing.
According to J. Hall (1970), in Ontario at least, the most widely used site preparation technique was post-harvest mechanical scarification by equipment front-mounted on a bulldozer (blade, rake, V-plow, or teeth), or dragged behind a tractor (Imsett or S.F.I. scarifier, or rolling chopper). Drag type units designed and constructed by Ontario’s Department of Lands and Forests used anchor chain or tractor pads separately or in combination, or were finned steel drums or barrels of various sizes and used in sets alone or combined with tractor pad or anchor chain units.
J. Hall’s (1970) report on the state of site preparation in Ontario noted that blades and rakes were found to be well suited to post-cut scarification in tolerant hardwood stands for natural regeneration of yellow birch. Plows were most effective for treating dense brush prior to planting, often in conjunction with a planting machine. Scarifying teeth, e.g., Young’s teeth, were sometimes used to prepare sites for planting, but their most effective use was found to be preparing sites for seeding, particularly in backlog areas carrying light brush and dense herbaceous growth. Rolling choppers found application in treating heavy brush but could be used only on stone-free soils. Finned drums were commonly used on jack pine–spruce cutovers on fresh brushy sites with a deep duff layer and heavy slash, and they needed to be teamed with a tractor pad unit to secure good distribution of the slash. The S.F.I. scarifier, after strengthening, had been “quite successful” for 2 years, promising trials were under way with the cone scarifier and barrel ring scarifier, and development had begun on a new flail scarifier for use on sites with shallow, rocky soils. Recognition of the need to become more effective and efficient in site preparation led the Ontario Department of Lands and Forests to adopt the policy of seeking and obtaining for field testing new equipment from Scandinavia and elsewhere that seemed to hold promise for Ontario conditions, primarily in the north. Thus, testing was begun of the Brackekultivator from Sweden and the Vako-Visko rotary furrower from Finland.
Site preparation treatments that create raised planting spots have commonly improved outplant performance on sites subject to low soil temperature and excess soil moisture. Mounding can certainly have a big influence on soil temperature. Draper et al. (1985), for instance, documented this as well as the effect it had on root growth of outplants (Table 30).
The mounds warmed up quickest, and at soil depths of 0.5 cm and 10 cm averaged 10 and 7 °C higher, respectively, than in the control. On sunny days, daytime surface temperature maxima on the mound and organic mat reached 25 °C to 60 °C, depending on soil wetness and shading. Mounds reached mean soil temperatures of 10 °C at 10 cm depth 5 days after planting, but the control did not reach that temperature until 58 days after planting. During the first growing season, mounds had 3 times as many days with a mean soil temperature greater than 10 °C than did the control microsites.
Draper et al.’s (1985) mounds received 5 times the amount of photosynthetically active radiation (PAR) summed over all sampled microsites throughout the first growing season; the control treatment consistently received about 14% of daily background PAR, while mounds received over 70%. By November, fall frosts had reduced shading, eliminating the differential. Quite apart from its effect on temperature, incident radiation is also important photosynthetically. The average control microsite was exposed to levels of light above the compensation point for only 3 hours, i.e., one-quarter of the daily light period, whereas mounds received light above the compensation point for 11 hours, i.e., 86% of the same daily period. Assuming that incident light in the 100-600 µEm‾²s‾1 intensity range is the most important for photosynthesis, the mounds received over 4 times the total daily light energy that reached the control microsites.
Orientation of linear site preparation, e.g., disk-trenching
With linear site preparation, orientation is sometimes dictated by topography or other considerations, but the orientation can often be chosen. It can make a difference. A disk-trenching experiment in the Sub-boreal Spruce Zone in interior British Columbia investigated the effect on growth of young outplants (lodgepole pine) in 13 microsite planting positions: berm, hinge, and trench in each of north, south, east, and west aspects, as well as in untreated locations between the furrows (Burton et al. 2000). Tenth-year stem volumes of trees on south, east, and west-facing microsites were significantly greater than those of trees on north-facing and untreated microsites. However, planting spot selection was seen to be more important overall than trench orientation.
In a Minnesota study, the N–S strips accumulated more snow but snow melted faster than on E–W strips in the first year after felling (Clausen and Mace 1972). Snow-melt was faster on strips near the centre of the strip-felled area than on border strips adjoining the intact stand. The strips, 50 feet (15.24 m) wide, alternating with uncut strips 16 feet (4.88 m) wide, were felled in a Pinus resinosa stand, aged 90 to 100 years.
- Hawley, R.C. and D.M. Smith. The Practice of Silviculture. 6th edition. New York: John Wiley & Sons Inc., 1954. Print.
- Ford-Robertson, F.C. (Ed.) 1971. Terminology of Forest Science, Technology, Practice and Products. English language version. Soc. Amer. For., Washington DC. 349 p.
- Köstler, J. 1956. Silviculture. Transl. M.L. Anderson from "Waldbau" (1949). Oliver and Boyd, Edinburgh and London, U.K. 416 p.
- Jeglum, J.K.; Kershaw, H.M.; Morris, D.M.; Cameron, D.A. 2003. Best forestry practives: A guide for the boreal forest in Ontario. Natural Resources Canada, Can. For. Serv., Sault Ste. Marie ON, co-published by Ont. Min. Nat. Resources, Sault Ste. Marie ON. 110 p.
- John D. Matthews, Silvicultural Systems. Oxford Science Publications. 1991, ISBN 9780198546702
- Lees, J.C. 1970. Natural regeneration of white spruce under spruce–aspen shelterwood, B-18a Forest Section, Alberta. Can. Dep. Fish. For., Can. For. Serv., Ottawa ON, Publ. 1274. 14 p.
- Stiell, W.M. 1976. White spruce: artificial regeneration in Canada. Dep. Environ., Can. For. Serv., Ottawa ON, Inf. Rep. FMR-X-85. 275 p.
- Greene, D.F.; Zasada, J.C.; Sirois, L.; Kneeshaw, D.; Morin, H.; Charron, L.; Simard, M.-J. 1999. A review of the regeneration dynamics of North American boreal forest tree species. Can. J. For. Res. 29:824–839.
- Sutton, R.F. 1992. White spruce (Picea glauca [Moench] Voss): stagnating boreal old-field plantations unresponsive to fertilization and weed control. For. Chron. 68:249–258.
- Grossnickle, S.C. 2000. Ecophysiology of northern spruce species: the performance of planted seedlings. NRC Research Press, Ottawa ON. 409 p.
- Template:11 Huss,J. 2004;
- Schopmeyer, C.S. (Tech. Coord.) 1974. Seeds of Woody Plants in the United States. USDA, For. Serv., Washington DC, Agric. Handb. 450. 883 p.
- MacArthur, J.D.; Fraser, J.W. 1963. Low temperature germination of some eastern Canadian tree seed. For. Chron. 39(4):478–479.
- Arnott, J.T. 1974. Germination and seedling establishment. p. 55–66 in Cayford, J.H. (Ed.). Direct Seeding Symposium, Timmins ON, Sept. 1973, Can. Dep. Environ., Can. For. Serv., Ottawa ON, Proc., Publ. 1339.
- Alexander, R.R. 1984. Natural regeneration of Engelmann spruce after clearcutting in the central Rocky Mountains in relation to environmental factors. USDA, For. Serv., Rocky Mountain For. Range Exp. Sta., Fort Collins CO, Res. Pap. RM-254. 17 p.
- Baldwin, H.I. 1927. A humus study in Norway. Ecology 8:380–383.
- Mork, E. 1933. [Temperature as a factor of regeneration in the spruce forests of Northern Trondhjem.] Meddelelser fra Det Norske Skogforsøkvesen No. 16 Vol. V, No. 1. [Reviewed in J. For. 32:1024, 1934]
- Rowe, J.S. 1955. Factors influencing white spruce reproduction in Manitoba and Saskatchewan. Can. Dep. Northern Affairs and National Resources, For. Branch, For. Res. Div., Ottawa ON, Project MS-135, Silv. Tech. Note 3. 27 p.
- Phelps, V.H. 1940a. Cut-over and burned-over white spruce lands, northern Saskatchewan survey, 1938. Can. Dep. Mines and Resources, Lands, Parks and For. Branch, Dominion For. Serv., Ottawa ON, unpubl. Report. (Cited in Rowe 1955, orig. not seen)
- Phelps, V.H. 1940b. Spruce regeneration in Canada -the Prairie Provinces. For. Chron. 16:30–37.
- Alexander, R.R. 1958. Silvical characteristics of Engelmann spruce. USDA, For. Serv., Rocky Mountain For. Range Exp. Sta., Fort Collins CO, Paper 31. 20 p.
- Sutton, R.F. 1991. Soil properties and root development in forest trees: a review. For. Can., Ont. Region, Sault Ste. Marie ON, Inf. Rep. O-X-413. 42 p.
- Alexander, R.R. 1983. Seed: seedling ratios of Engelmann spruce after clearcutting in the central Rocky Mountains. USDa For. Serv., Rocky Mountain Forest and Range Exp. Sta., Fort Collins, CO. Research Note RM-426. 6 p.
- Baldwin, H.I. 1942. Forest Tree Seed. Chronica Botanica, Waltham MA. 240 p.
- Baldwin, H.I. 1933. The density of spruce and fir reproduction related to the direction of exposure. Ecology 14:152–156.
- Alarik, A. 1925. Moderna huggningsformer tillämpade pâ Finspång. Skogen 12:211–243.
- Hartley, C. 1918. Stem lesions caused by excessive heat. J. Agric. Res. 14:595–604.
- Eis, S.; Inkster, J. 1972. White spruce cone production and prediction of cone crops. Can. J. For. Res.2:460–466.
- Noble, D.L.; Ronco, F. 1978. Seedfall and establishment of Engelmann spruce and subalpine fir in clearcut openings in Colorado. USDA, For. Serv., Rocky Mountain For. Range Exp. Sta., Res. Pap. RM-200. 12 p.
- Radvanyi, A. 1970. Small mammals and regeneration of white spruce forests in western Alberta. Ecology 51(6):1102–1105.
- Coates, K.D.; Haeussler, S.; Lindeburgh, S.; Pojar, R.; Stock, A.J. 1994. Ecology and silviculture of interior spruce in British Columbia. Canada/British Columbia Partnership Agreement For. Resour. Devel., Victoria BC, FRDA Rep. 220. 182 p.
- Gilmour, J.G.; Konishi, J. 1965. Scarification in the spruce alpine fir type of the Prince George Forest District. Preliminary evaluation of methods and resulting regeneration.B.C. For. Serv., Victoria BC, For. Manage. Notes 4. (Cited in Coates et al. 1994).
- Ackerman, R.F. 1957. The effect of various seedbed treatments on the germination and survival of white spruce and lodgepole pine seedlings. Can. Dep. Northern Affairs & National Resour., For. Branch, Ottawa ON, Tech. Note 63. 23 p.
- Zasada, J.C. 1985. Production, dispersal and germination, and first-year seedling survival of white spruce and birch in the Rosie Creek burn. p.34–37 in Juday, G.P.; Dyrness, C.T. (Eds.), Early Results of the Rosie Creek Fire Research Project, 1984. Univ. Alaska, Agric. For. Exp. Sta., Fairbanks AK, Misc. Publ. 85–2.
- Zasada, J. 1986. Natural regeneration of trees and tall shrubs on forest sites in interior Alaska. p. 44–73 in Van Cleve, K.; Chapin, F.S.; Flanagan, P.W.; Viereck, L.A.; Dyrness, C.T. (Eds.). Forest Ecosystems in the Alaskan Taiga: a Synthesis of Structure and Function. Springer-Verlag New York NY.
- Zasada, J.C.; Norum, R. 1986. Prescribed burning white spruce slash in interior Alaska. North. J. Appl. For. 3(1):16–18.
- Bell, F.W. 1991. Critical silvics of conifer crop species and selected competitive vegetation in northwestern Ontario. For. Can., Sault Ste. Marie, Ont./Ont. Min. Nat. Resour., Northwestern Ont. For. Tech. Devel. Unit, Thunder Bay ON, COFRDA Rep. 3310/ NWOFTDU Tech. Rep. 19. 177 p.
- Sutton, R.F. 1984. Plantation establishment in the boreal forest: glyphosate, hexazinone, and manual weed control. For. Chron. 60:282–287.
- Toumey, J. W. and Korstian, C.F. 1942. Seeding and planting in the forestry practice. Ed. 3. John Wiley & Sons Inc., New York.
- Sutton, R.F. 1969. Form and development of conifer root systems. Commonw. For. Bureau, Oxford, U.K., Tech. Communication No. 7. 131 p.
- Mullin, R.E. 1971. Some effects of root dipping, root exposure and extended planting dates with white spruce. For. Chron. 47(2):90–93.
- Kittredge, J. 1929. Forest planting in the Lake States. U.S.D.A., For. Serv., Washington DC, Agric. Bull. 1497. 87 p.
- LeBarron, R.K.; Fox, G.; Blythe, R.H. 1938. The effect of season of planting and other factors on early survival of forest plantations. J. For. 36:1211–1215.
- Rudolf, P.O. 1950. Cold soaking – a short-cut substitute for stratification? J. For. 48(1):31–32.
- Mullin, R.E. 1968. Comparisons between seedlings and transplants in fall and spring plantings. Ont. Dep. Lands For., Res. Div., Toronto ON, Res. Rep. 85. 40 p.
- Sinclair, C.; Boyd, R.J. 1973. Survival comparisons of three fall and spring plantings of four coniferous species in northern Idaho. USDA, For. Serv., Intermount. For. Range Exp. Sta., Ogden UT, Res. Pap. INT-139. 20 p.
- McClain, K.M. 1975. Continuous planting of seedling black spruce. p. 177–194 in Black Spruce Symp. Proc., Can. Dep. Environ., Can. For. Serv., Sault Ste. Marie ON, Symp. Proc. O-P-4.
- McClain, K.M. 1979. A review on the possibility of extending the planting season. Ont. Min. Nat. Resour., Northern For. Res. Unit, Thunder Bay ON. 44 p.
- Crossley, D.I. 1956. The possibility of continuous planting of white spruce throughout the frost-free period. Can. Dep. Northern Affairs National Resour., For. Branch, For. Res. Div., Ottawa ON, Tech. Note 32. 31 p.
- Revel, J.; Coates, H. 1976. Planting white spruce throughout the growing season on high site areas in the Sub-Boreal Forest Region of B.C. B.C. For. Serv., Res. Div., Victoria BC, Rep. E.P.668. 37 p.
- Burgar, R.J.; Lyon, N.F. 1968. Survival and growth of stored and unstored white spruce planted through the frost-free period. Ont. Dep. Lands Forests, Toronto ON, Res. Rep. 84. 37 p.
- Mullin, R.E. 1974. Some planting effects still significant after 20 years. For. Chron. 50:191–193.
- Mullin, R.E. 1978. Tests of frozen spring storage for white spruce and red pine planting stock. USDA, For. Serv., Tree Plant. Notes 29(4):26–29.
- Mullin, R.E.; Forcier, L. 1976. Effect of lifting and planting dates on survival and growth of spring stored nursery stock. Ont. Min, Nat. Resour., For. Res. Branch, Toronto ON, For. Res. Notes 3. 4 p.
- Mullin, R.E.; Reffle, R.J. 1980. Effects of dates of lifting and planting on success of frozen spring storage at Swastika Nursery. Ont. Min, Nat. Resour., Toronto ON, Nursery Notes 66. 5 p.
- Mullin, R.E.; Parker, J.D. 1976. Provisional guidelines for fall lifting for frozen overwinter storage of nursery stock. For. Chron. 52(1):22–25.
- Jorgensen, E.; Stanek, W.K.L. 1962. Overwinter storage of coniferous seedlings as a means of preventing late frost damage. For. Chron. 38(2):192–202.
- Mullin, R.E. 1966. Overwinter storage of baled nursery stock in northern Ontario. Commonw. For. Rev. 45(3):224–230.
- Anon. 1961. Northern conifer planting stock produced under long photoperiods in Florida. p. 9–13 in 1960 Rep., Lake States For. Exp. Sta.
- Nienstaedt, H.; Zasada, J.C. 1990. Picea glauca (Moench) Voss. p. 204–226 in Burns, R.M. and Honkala, B.H. (Tech. Coord.), Silvics of North America, Vol. 1, Conifers. USDA, For. Serv., Washington DC, Agric. Handbook 654.
- Pollard, D.F.W.; Logan, K.T. 1976. Prescription for the aerial environment for a plastic greenhouse nursery. p.181–191 in Proc. 12th Lake States For. Tree Improv. Conf. 1975. USDA, For. Serv., North Central For. Exp. Sta., St. Paul MN, Gen. Tech. Rep. NC-26.
- Carlson, L.W. 1979. Guidelines for rearing containerized conifer seedlings in the prairie provinces. Can. Dep. Environ., Can. For. Serv., Edmonton AB, Inf. Rep. NOR-X-214. 62 p. (Cited in Nienstaedt and Zasada 1990).
- Tinus, R.W.; McDonald, S.E. 1979. How to grow tree seedlings in containers in greenhouses. USDA, For. Serv., Rocky Mountain For. Range Exp. Sta., Fort Collins CO, Gen. Tech. Rep. RM-60. 256 p. (Cited in Nienstaedt and Zasada 1990).
- Tinus, R.W. 1984. Optimum temperatures for growth of southern Rocky Mountain Engelmann spruce and Douglas-fir seedlings. USDA, For. Serv., Rocky Mount. For. Range Exp. Sta., Fort Collins CO, Res. Note RM-442. 5 p.
- Tappeiner, J.C., D.A. Maguire, and T.B. Harrington. Silviculture and Ecology of Western U.S. Forests. Corvallis: Oregon State University Press, 2007. Print.
- Joyce, D.; Nitschke, P.; Mosseler, A. 2001. Genetic resource management. p. 141–154 in Wagner, R.G.; Colombo, S.J. (Eds.). Regenerating the Canadian Forest: Principles and Practice for Ontario. Fitzhenry and Whiteside, Markham ON.
- Hills, G.A. 1952. The classification and evaluation of site for forestry. Ont. Dep. Lands For., Res. Div., Toronto ON, Res. Rep. 24. 41 p.
- Mackey, B.G.; McKenney, D.W.; Yang, Y.Q.; McMahon, J.P., and Hutchinson, M.F. 1996. Site regions revisited: a climatic analysis of Hills’ site regions for the province of Ontario using a parametric method. Can. J. For. Res. 26:333–354.
- [OMNR] Ontario Ministry of Natural Resources. 1997. Seed zones of Ontario. Toronto ON, Policy Directive No. FOR 03 02 06 500 02. 5 p. [Cited by Joyce et al. 2005, original not seen]
- Li, P.; Beaulieu, J.; Bousquet, J. 1997. Genetic structure and patterns of genetic variation among populations in eastern white spruce (Picea glauca). Can. J. For. Res. 27:189–198.
- Toumey, J.W.; Korstian, C.F. 1954. Seeding and Planting in the Practice of Forestry., 3rd ed. Wiley & Son, New York NY. 520 p.
- Wang, B.S.P. 1973. Collecting, processing and storing tree seed for research use. IUFRO International Symposium on Seed Processing, Bergen, Norway, 1973: Vol. 1:17. 11 p.
- Noland, T.L.; Mohammed, G.H.; Seymour, N. 2001. Testing tree seed viability with FDA: what does it tell you? p. 23 in Proc. Working together for our common future. LUSTR Co-op. Ann. Gen. Meet. & Workshop, Feb. 2001, Timmins ON.
- Timonin, M.I. 1966. Effect of ultra-sound on the germination of white spruce and jack pine. Can. J. Bot. 44:113–115. (Cited in Coates et al. 1994).
- Rafn, J. 1915. The testing of forest seeds during 25 years, 1887–1912. Copenhagen, Denmark. 91 p. (Cited in Toumey and Korstian 1954, orig. not seen)
- Mittal, R.K.; Wang, B.S.P. 1987. Fungi associated with seeds of eastern white pine and white spruce during cone processing and seed extraction. Can. J. For. Res. 19(9):1026–1034.
- Haddon, B.D.; Winston, D.A. 1982. Germination after two years storage of artificially ripened white spruce seed. p. 75–80 in Wang, B.S.P.; Pitel, J.A. (Eds.). Proc. Internat. Sympos. Forest Tree Seed Storage, Sept. 1980, Chalk River ON. Environ. Can., Can. For. Serv. (Cited in Coates et al. 1994).
- Wang, B.S.P. 1974a. Testing and treatment of Canadian white spruce seed to overcome dormancy. Assoc. Official Seed Analysts Proc. 64:72–79.
- Zasada, J.C.; Foote, M.J.; Deneke, F.J.; Parkerson, R.H. 1978. Case history of an excellent white spruce cone and seed crop in interior Alaska: cone and seed production, germination and seedling survival. USDA, For. Serv., Pacific NW For. Range Exp. Sta., Portland OR, Gen. Tech. Rep. PNW-65. 53 p.
- Armson, K.A.; Sadreika, V. 1979. Forest tree nursery soil management and related practices – metric edition. Ont. Min. Nat. Resour., Div. For. For. Manage. Branch, Toronto ON. 179 p.
- Simpson, J.D.; Wang, B.S.P.; Daigle, B.I. 2004. Long-term storage of various Canadian hardwoods and conifers. Seed Sci. & Technol. 32:561–572.
- Heit, C.E. 1961. Laboratory determination and recommended testing methods for 16 spruce (Picea) species. p. 165–171 in Assoc. Off. Seed Anal. 51st Annu. Meet. Proc. (Cited in Coates et al. 1994).
- Hellum, A.K. 1968. A case against cold stratification of white spruce seed prior to nursery seeding. Can. Dep. For. and Rural Devel., For. Branch, Ottawa ON, Publ. 1243. 12 p.
- van den Driessche, R. 1969. Forest nursery handbook. B.C. For. Serv., Victoria BC, Res. Notes 48. 44 p.
- Santon, J. 1970. Effect of stratification on germination of freshly harvested seed of several spruce and pine species in eastern Canada. Can. Dep. Fish. For., Can. For. Serv., Petawawa For. Exp. Sta., Chalk River ON, Inf. Rep. PS-X-17. 22 p.
- Wang, B.S.P. 1987. The beneficial effects of stratification on germination of tree seeds. p. 56–75 in Proc. Nurserymen’s Meeting, Dryden ON, June 15–19, 1987. OMNR, Toronto ON.
- Hocking, D. 1972. Effects of stratification of Alberta white spruce and lodgepole pine seeds on emergence in operational seedbeds. Environ. Can., Can. For. Serv., Ottawa ON, Bi-mo. Res. Notes 28(4):26–27.
- Winston, D.A.; Haddon, B.D. 1981. Effects of early cone collection and artificial ripening on white spruce and red pine germination. Can. J. For. Res. 11:817–826.
- Kolotelo, D. 1997. Anatomy and morphology of conifer tree seed. Forest Nursery Technical Series 1.1 B.C. Min. for., 70 p.
- Mercier, S. 1991. Maturation et indices de maturité des semences d’épinette blanche. [Maturation and maturity indexes of white spruce seeds.] Quebec Min. For., Quebec QC, Memoire Rech. For. 103. 62 p. [Fr.e.; E 4085]
- Caron, G.E.; Wang, B.S.P.; Schooley, H.O. 1990. Effect of tree spacing, cone storage, and prechilling on germination of Picea glauca seed. For. Chron. 66(4):388–392.
- Caron, G.E.; Wang, B.S.P.; Schooley, H.O. 1993. Variation in Picea glauca seed germination associated with the year of cone collection. Can. J. For. Res. 23(7):1306–1313.
- Armson, K.A.; Carman, R.D. 1961. Forest tree nursery soil management. Ont. Dep. Lands & Forests, Timber Branch, Ottawa ON. 74 p.
- Armson, K.A. 1966. The growth and absorption of nutrients by fertilized and unfertilized white spruce seedlings. For. Chron. 42(2):127–136.
- Duryea, M.L.; McClain, K.M. 1984. Altering seedling physiology to improve reforestation success. pp. 77–114 in M.L. Dryea and G.N. Brown (eds.). Seedling physiology and reforestation success. Martinus Nijhoff/Dr. W. Junk, The Hague.
- Dobbs, R.C. 1976. Effect of initial mass of white spruce and lodgepole pine planting stock on field performance in the British Columbia Interior. Can. Dep. Environ., Can. For. Serv., Victoria BC, Inf. Rep. BC-X-149. 14 p.
- McMinn, R.G. 1985a. Effect of initial mass on the field performance of white spruce planting stock. Can. For. Serv., Victoria BC, File Rep. PC 48-357, Exp. 72-F2. 5 p.
- McMinn, R.G. 1980. Root growth capacity and field performance of various types and sizes of white spruce stock following outplanting in the central interior of British Columbia. p. 37–41 in Schmidt-Vogt, H. (Ed.). Characterization of Plant Material. Proc. IUFRO Working Group S1.05-04 Meet., Waldbau-Institut, Univ. Freiburg, Germany.
- McMinn, R.G. 1984. Field performance of various sizes of white spruce stock in recently cut and backlog sites. Can. For. Serv., Victoria BC, File Rep. PC 48-357, Exp. 78-F1. 4 p.
- Paterson, J.M.; Hutchison, R.E. 1989. Red pine, white pine, white spruce stock type comparisons. Ont. Min. Nat. Resour., For. Res. Note 47. 4 p.
- Lajzerowicz, C.C., Vyse, A., Jull, M., and Newsome, T. 2006. Performance of planted Engelmann spruce and subalpine fir seedlings in British Columbia’s southern mountains. For. Chron. 82(1):84–94
- Thompson, C. 1995. Preliminary height expectations of Engelmann spruce plantations for three elevations in the Nelson Forest Region. B.C. Min. For. Nelson For. Region, Res. Sum RS-020. (Cited by Lajzerowicz et al. 2006, orig. not seen.)
- Willen, P.; Sutton, R.F. 1980. Evaluation of planting stock quality: Evaluation of stock after planting. New Zealand J. For. Sci. 10:297–299.
- Sutton, R.F. 1987. Plantation establishment in boreal Ontario: a study of spring planting and mechanization. Gov’t Can., Can. For. Serv., Sault Ste. Marie ON, Inf. Rep. O-X-383. 26 p.
- Wakely, P.C. 1954. Planting the southern pines. USDA For. Serv.. Monograph 18. 233 p.
- Tucker, R.E.; Jarvis, J.M.; Waldron, R.M. 1968. Early survival and growth of white spruce plantations, Riding Mountain National Park, Manitoba. Can. Dep. For. Rural Devel., For. Branch, Ottawa ON, Publ. 1239. 26 p.
- Morrison, I.K.; Armson, K.A. 1968. The rhizometer – a new device for measuring roots of tree seedlings. For. Chron. 44: 21-23.
- Burdett, A.N. 1979. New methods for measuring root growth capacity: their value in assessing lodgepole pine stock quality. Can. J. For. Res. 9:63–67.
- Helgerson, O.T. 1990. Heat damage in tree seedlings and its prevention. New For. 3:333–358.
- Colombo, S.J.; Timmer, V.R.; Colclough, M.L.; Blumwald, E. 1995. Diurnal variation in heat tolerance and heat shock protein expression in black spruce (Picea mariana). Can. J. For. Res. 25(3):369–375.
- Key, J.L.; Lin, C.Y.; Chen, Y.M. 1981. Heat shock proteins of higher plants. Proc. U.S. Acad. Sci. 78:3526–3530.
- Kimpel, J.A.; Key, J.L. 1985a. Heat chock in plants. Trends Biochem. Sci. 10:353–357.
- Kimpel, J.A.; Key, J.L. 1985b. Presence of heat shock mRNAs in field grown soybeans. Plant Physiol. 79:672–678.
- Coclough, M.L. 1991. The induction of thermotolerance and heat shock protein synthesis in Picea mariana seedlings by heat conditioning. M.Sc. Thesis, University of Toronto, Toronto, Ontario.
- Colombo, S.J.; Colclough, M.L.; Timmer, V.R.; Blumwald, E. 1992. Clonal variation in heat tolerance and heat shock protein expression in black spruce. Silvae Gent. 41:234–239.
- Hambly, E.S.L. 1973. The periodicity of root regeneration potential of black and white spruce and jack pine nursery seedlings. M.Sc. thesis, Univ. Toronto, Fac. For., Toronto ON. 66 p.
- Day, R.J.; MacGillivray, G.R. 1975. Root regeneration of fall-lifted white spruce nursery stock in relation to soil moisture content. For. Chron. 51:196–199.
- Day, R.J.; Breunig, E. 1997. Root generation of 3+0 white spruce varies with root system size, post-planting moisture and climate. B.Sc.F. Thesis, Lakehead University, Thunder Bay, Ontario. 38 p.
- Stone, E.C. 1955. Poor survival and the physiological condition of planting stock. For. Sci. 1:90–94.
- Simpson, D.G.; Ritchie, G.A. 1997. Does RGP predict field performance? A debate. New For. 13:253–277.
- Scagel, C.F.; Linderman, R.G. 2001. Modification of root IAA concentrations, tree growth, and survival by application of plant growth regulating substances to container-grown conifers. New For. 21:159–186.
- Grossnickle, S.C. 1988. Planting stress in newly planted jack pine and white spruce. I. Factors influencing water uptake. Tree Physiol. 4(1):71–84. [Search 8 abstr 38 of 99]
- Grossnickle, S.C.; Blake, T.J. 1986. Environmental and physiological control of needle conductance for bare-root black spruce, white spruce, and jack pine seedlings on boreal cutover sites. Can. J. Bot. 64(5):943–949.
- Grossnickle, S.C.; Blake, T.J. 1987. Water relation patterns of bare-root and container jack pine and black spruce seedlings planted on boreal cut-over sites. New For. 1:101–116.
- Marsden, B.J.; Lieffers, V.J.; and Zwiazek, J.J. 1996. The effect of humidity on photosynthesis and water relations of white spruce seedlings during the early establishment phase. Can. J. For. Res. 26(6):1015–1021.
- Candy, R.H. 1929. Seedlings versus transplants at Petawawa Forest Experiment Station. For. Chron. 5(4):17–20.
- Korstian, C.F.; Baker, F.S. 1925. Forest planting in the Intermountain region. USDA, For. Serv., Washington DC, Agric. Bull. 1264. 56 p.
- Cleary, B.D.; Greaves, R.D.; Hermann, R.K. (Compilers and Eds.). 1978. Regenerating Oregon’s Forests. Oregon State Univ. Exten. Serv., Corvallis OR. 287 p.
- Duryea, M.L.; Landis, T.D. (Eds.) 1984. Forest Nursery Manual: Production of Bareroot Seedlings. Nijhoff/Junk, Boston MA. 386 p.
- Lavender, D.P.; Parish, R.; Johnson, C.M.; Montgomery, G.; Vyse, A.; Willis, R.A.; Winston, D. (Eds.). 1990. Regenerating British Columbia’s Forests. Univ. B.C. Press, Vancouver BC. 372 p.
- Wagner, R.G.; Columbo, S.J. (eds.). 2001. Regenerating the Canadian forest: Principles and practice for Ontario. Fitzhenry & Whiteside, Markham, Ont.
- Ontario Class Environmental Assessment for Timber Management. 1989. Ont. Min. Nat. Resour. Witness Statements, Evidence Panels I to XVII. Compiled 1989.02,22, Sections separately paginated.
- British Columbia. Ministry of Forests. 1995. Forest practices code of British Columbia: Silvicultural systems guidebook. BC MoF, BC Ministry of Environment, 44 p.
- Milthorpe, F.L. 1961. The nature and analysis of competition between plants of different species. p. 330–355 in Mechanisms in Biological Competition. Sympos. Soc. Exp. Biol. 15, Cambridge Univ. Press, Cambridge, U.K.
- Buse, L.J.; Baker, W.D. 1991. Determining necessity and priority for tending in young spruce plantations in northwestern Ontario. Ont. Min. Nat. Resour., Northwestern Ont. For. Technol. Devel. Unit, Thunder Bay ON, Tech. Note TN-08. 4 p.
- Simard, S. 1966. 1996. Mixtures of paper birch and conifers: An ecological balancing act. pp. 15-22 In: P.G. Comeau & K.D. Thomas (eds.) Silviculture of temperate boreal broadleaf-conifer mixtures. BC Ministry of Forests, Research Branch, Victoria, BC. Land Management Handbook 36.
- Green, D.S. 2004. Describing condition-specific determinants of competition in boreal and sub-boreal mixedwood stands. For. Chron. 80(6):736–742.
- Lieffers, V.J.; Pinno, B.; Stadt, K.J. 2002. Light dynamics and free-to-grow standards in aspen-dominated mixedwood forests. For. Chron. 78(1):137–145.
- Bella, I.E. 1971. A new competition model for individual trees. For. Sci. 17:364–372.
- Hegyi, F. 1974. A simulation model for managing jack pine stands. p. 74–90 in Fries, J. (Ed.). Growth Models for Tree and Stand Simulation. R. Coll. For., Dep. For. Yield Res., Res. Note 30.
- Ek, A.R.; Monserud, R.A. 1974. Trials with program FOREST: Growth and reproduction simulation of mixed species forest stands. p. 56–73 in Fries, J. (Ed.). Growth Models for Tree and Stand Simulation. R. Coll. For., Dep. For. Yield Res., Res. Note 30.
- Howard, K.M.; Newton, M. 1984. Overtopping by successional coast range vegetation slows Douglas-fir seedlings. J. For. 82:178–180.
- Daniels, R.F. 1976. Simple competition indices and their correlation with annual loblolly pine tree growth. For. Sci. 22:454–456.
- Weiner, J. 1984. Neighbourhood interference amongst Pinus rigida individuals. J. Ecol. 72:183–195.
- Zedaker, S.M. 1982. Growth and development of young Douglas-fir in relation to intra- and inter-specific competition. Oregon State Univ., Corvallis OR, Ph.D. thesis. (Cited by Morris and MacDonald 1991, orig. not seen.)
- Brand, D.G.; Kehoe, P.; Connors, M. 1986. Coniferous afforestation leads to soil acidification in central Ontario. Can. J. For. Res. 16(6):1389–1391.
- Smith, D.M. 1962. The Practice of Silviculture, 7th ed. Wiley & Sons, New York NY. 378 p.
- [OMNR] Ontario Mnistry of Natural Resources. 1989. Operational guidelines for tree improvement in Ontario. Ont. Min. Nat. Resour., Toronto ON, 9 sections separately paginated.
- Drew, J.T.; Flewelling, J.W. 1979. Stand density management: an alternative approach and its application to Douglas-fir plantations. For. Sci. 25:518–532.
- Archibald, D.J.; Bowling, C. 1995. Jack pine density management diagram for boreal Ontario. Ont. Min. Nat. Resour., Northeast Science & Technology, Tech. Note TN-005 NWST TN-31. 20 p.
- Smith, N.J.; Brand, D.G. 1988. Compatible growth models and stand density diagrams. p. 636–643 in Ek. A.R..; Shifley, S.R..; Burk, T.E. (Eds.). Forest Growth Modelling and Prediction. Vol. 2. Proc. IUFRO Conf., August 1987, Minneapolis MN.
- Template:5 Keefe,K. 2012;
- 'Fact Sheet 4.12. Forest Regeneration', IPCC Special Report on Land Use, Land-Use Change And Forestry
- Daniel, Theodore, John Helms, and Frederick Baker. Principles of Silviculture. 2nd ed. New York: McGraw-Hill, 1979. Print.
- Lloyd, G.D. 1991. Juvenile spacing in rgw sub-boreal spruce biogeoclimatic region of British Columbia. p. 20–26 in Haavisto, V.F.; Smith, C.R.; Mason, C. (Eds.). Space to grow: spacing and thinning in northern Ontario. Proc. sympos., June 1990, Sault Ste. Marie ON, For. Can., Ont. Region/Ont. Min. Nat. Resour. Joint Rep. 15.
- Hermelin, J. 1991. Spacing in eastern Canada: the New Brunswick experience. p. 27–29 in Haavisto, V.F., Smith, C.R.; Mason, C. (Eds.). Space to grow: spacing and thinning in northern Ontario. Proc. Sympos., June 1990, Sault Ste. Marie ON, For. Can., Ont. Region/Ont. Min. Nat. Resour. Joint Rep. 15.
- Nicks. B.D. 1991. A company perspective on spacing and thinning. p. 62–67 in Haavisto, V.F.; Smith, C.R.; Mason, C. (Eds.). Space to grow: spacing and thinning in northern Ontario. Proc. sympos., June 1990, Sault Ste. Marie ON, For. Can., Ont. Region/Ont. Min. Nat. Resour. Joint Rep. 15.
- Ker, M.F. 1981. Early response of balsam fir to spacing in northwestern New Brunswick. Environment Canada, Canadian Forestry Service, Maritimes Forestry Centre, Fredericton, New Brunsick, Information Report M-X-129, 36 p.
- Bella, I.E. 1986. Spacing effects 20 years after planting three conifers in Manitoba. Can., Can. For. Serv., Edmonton AB, For. Manage. Note No. 39. 11 p.
- Bella, I.E.; De Franceschi, J.P. 1980. Spacing effects 15 years after planting three conifers in Manitoba. Can. Dep. Environ., Can. For. Serv., Northern For. Res. Centre, Edmonton AB, Inf. Rep. NOR-X-223. 10 p.
- Template:6 Savill,P.S. 2004;
- Baker, Frederick. Theory and Practice of Silviculture. First Edition. New York: McGraw-Hill, 1934. Print.
- Template:7 D’Amato,Anthony W. 2011;
- Day, M.W. 1967. Pre-commercial thinning in conifers with silvicides. Michigan State Univ., Agric. Exp. Sta., East Lansing MI, Quarterly Bull 50:59–62.
- The Dictionary of Forestry, The Society of American Foresters
- Smith, D.M., B.C. Larson, M.J. Kelty, and P.M.S. Ashton. The Practice of Silviculture: Applied Forest Ecology. 9th edition. New York: John Wiley & Sons, Inc., 1997. Print.
- Wright, T.G. 1959. The Canadian spruce forest. For. Chron. 35(4):291–297.
- Davis, L.S.; Johnson, K.N. 1987. Forest Management, 3rd ed. McGraw-Hill, New York, NY. 790 p.
- Burgess, D.; Larocque, G.R.; Brand, D.G. 2001. Forest growth and future yields: the importance of today’s regeneration practices. P. 603–624 in Wagner, R.G.; Colombo, S.J. (Eds.). Regenerating the Canadian Forest: Principles and Practice for Ontario. Fitzhenry & Whiteside, Markham ON in co-operation with Ont. Min. Nat. Resour. 650 p.
- Hearnden, K.W.; Millson, S.V.; Wilson, W.C. 1996. Ontario Independent Forest Audit Committee. Ont. Min. Nat. Resour., Sault Ste. Marie ON. 117 p.
- Waldron, R.M. 1966. Factors affecting natural white spruce regeneration on prepared seedbeds at the Riding Mountain Forest Experimental Area, Manitoba. Can. Dep. For. Rural Devel., For. Branch, Ottawa ON, Deptl. Publ. 1169. 41 p.
- Butt, G.; Bancroft, B.; Folk, R. 1989. Ingress of Engelmann spruce and subalpine fir in southern interior ESSF. For. Can./B.C. Min. For., Victoria BC, Project 3.61, unpub. rep. (Cited in Coates et al. 1994)
- Youngblood, A.P.; Zasada, J.C. 1991. White spruce artificial regeneration options on river floodplains in interior Alaska. Can. J. For. Res. 21(4):423–433.
- Herring, L.J.; McMinn, R.G. 1980. Natural and advanced regeneration of Engelmann spruce and subalpine fir compared 21 years after site treatment. For. Chron. 56:55–57.
- McMinn, R.G. 1986. Comparative productivity of seedbed, natural and planted regeneration following various site treatments in white spruce clearcuts. p. 31–33 in Murray, M. (Ed.), The Yield Advantages of Artificial Regeneration at High Latitudes. Proc. 6th Internat. Workshop on Forest Regeneration. USDA, For. Serv., Pacific Northwest For. Range Exp. Sta., Gen. Tech. Rep. PNW-194. 60 p. (Cited in Coates et al. 1994).
- Roussel, L. 1948. Couvert et photométrie. Bull. Soc. Forest Franche-Comté 25:313–326. For. Abs. 10:458–459, 1949.
- Reifsnyder, W.E.; Lull, H.W. 1965. Radiant Energy in Relation to Forests. USDA, For. Serv. Washington DC, Tech. Bull. 1344. 111 p.
- Oregon State University Extension Service
- RESIDUAL DAMAGE IN A CONIFER STAND THINNED WITH A CTL SYSTEM, University of Idaho
- Template:8 Bauhus,Jürgen 2009;
- Sauder, E.A. 1996. Techniques to maintain a windfirm understory. p. 31 in FERIC West, Vancouver BC, Work Program 1996.
- Effects of Group-Selection Opening Size on Breeding Bird Habitat Use in a Bottomland Forest. Christopher E. Moorman and David C. Guynn Jr. Ecological Applications , Vol. 11, No. 6 (Dec., 2001), pp. 1680-1691. Web. 4 Oct. 2013.
- Template:9 Schulte,Benedict J. 1998;
- Template:12 Gamborg,Christian 2003;
- Kubin, E.; Kemppainen, L. 1991. Effect of clearcutting of boreal spruce forest on air and soil temperature conditions. Acta Forestalia Fennica No. 225. 42 p.
- Smith, D.M., B.C. Larson, M.J. Kelty, P.M.S. Ashton (1997) The Practice of Silviculture: Applied Forest Ecology, John Wiley & Sons, p. 340-46
- Template:10 Harmer,R. 2004;
- Prochnau, A.E. 1963. Direct seeding experiments with white spruce, alpine fir, Douglas fir and lodgepole pine in the central interior of British Columbia. B.C. Min. For. Lands, Victoria BC, MOFL No. 37, Res Note. 24 p. (Cited in Coates et al. 1994).
- Smith, J.H.G.; Clark, M.B. 1960. Growth and survival of Engelmann spruce and alpine fir on seed spots at Bolean Lake, B.V. 1954–59. For. Chron. 36(1):46–49, 51. (Cited in Coates et al. 1994).
- Biolley, H. 1920. L’aménagement des forêts par la méthode expérimentale et spécialement la méthode du contrôle. Paris, Attinger frères. 90 p.
- Gardner, A.C. 1980. Regeneration problems and options for white spruce on river floodplains in the Yukon Territory. p. 19–24 in Murray, M.; Van Veldhuizen, R.M. (Eds.). Forest Regeneration at High,
- Weetman, G.; Vyse, A. 1990. Natural regeneration. p. 118–130 in Lavender, D.P.; Parish, R.; Johnson, C.M.; Montgomery, G.; Vyse, A.; Willis, R.A.; Winston, D. (Eds.). Regenerating British Columbia’s Forests. Univ. B.C. Press, Vancouver BC. (Cited in Coates et al. 1994).
- Glew, D.R. 1963. The results of stand treatment in the white spruce–alpine fir type of the northern interior of British Columbia. B.C. Dep. Lands For. Water Resour., B.C. For. Serv., Victoria BC, For. Manage. Note 1. 27 p. (Cited in Coates et al. 1994).
- Zasada, J.C. 1972. Guidelines for obtaining natural regeneration of white spruce in Alaska. USDA, For. Serv., Pacific Northwest For. Range Exp. Sta., Portland OR. 16 p.
- Lähde, F. and Tuohisaari, O. 1976. An ecological study on the effects of shelters on germination and germling development of Scotch pine, Norway spruce and Siberian larch. Comm. Inst. For. Reprint 88.1. 35 p.
- Putman, W.E.; Zasada, J.C. 1986. Direct seeding techniques to regenerate white spruce in interior Alaska. Can. J. For. Res. 16(3):660–664.
- Putman, W.E.; Zasada, J.C. 1985. Raven damage to plastic seeding shelters in interior Alaska. North. J. Appl. For. 2(2):41–43. (Cited in Coates et al. 1994).
- Dyck, J.R. 1994. Converting aspen stands to white spruce–aspen mixedwoods by planting and seeding, Manitoba: Manitoba forestry demonstration areas. Can./Manitoba Partnership in For., unumbered rep. 28 p.
- Template:3 Brose,Patrick H. 2008; 3 Brose,Patrick H. 2008;
- Template:4 Holgén,Per 2000; 4 Holgén,Per 2000;
- Survival and Growth of Under-Planted Trees: A Meta-Analysis across Four Biomes. Alain Paquette, André Bouchard and Alain Cogliastro Ecological Applications , Vol. 16, No. 4 (Aug., 2006), pp. 1575-1589
- Template:4 Holgén,Per 2000;
- Alexander, R.R. 1973. Partial cutting in old-growth spruce-fir. USDA For. Serv., Rocky Mountain and Range Exp. Sta., Fort Collins, CO, Research Paper RM-100. 16 p.
- Conservation Approaches for Woody, Early Successional Communities in the Eastern United States. Frank R. Thompson, III and Richard M. DeGraaf Wildlife Society Bulletin , Vol. 29, No. 2 (Summer, 2001), pp. 483-494. Web. 4 October 2013.
- Robertson, W.M. 1927. Cutting for reproduction in spruce stands. For. Chron. 3(3):7–10.
- Scott, J.D. 1970. Direct seeding in Ontario. For. Chron. 46(6):453–457.
- Butt, G. 1988. Backlog forest land rehabilitation in the SBS and BWBS zones in the northern interior of British Columbia. Can./B.C. FRDA Rep. 023. 125 p.
- Dyer, E.D.A.; Taylor, D.W. 1968. Attractiveness of logs containing female spruce beetles Dendroctontus obesus (ColeopteraL Scolytidae). Can. Entomol 100: 769-776.
- DeLong, C. 1991. Dynamics of boreal mixedwood ecosystems. p.30–31 in Northern Mixedwood ‘89: Proceedings of a symposium held at Fort St. John, B.C., Sept. 1989. A. Shortreid (Ed.), For. Can., Pacific For. Centre, Victoria BC, FRDA Report 164.
- Kohm, K. A, and Franklin, J. F., Creating a forestry for the 21st century: the science of ecosystem management. Island Press. 1997, ISBN 978-1-55963-399-4
- The Role of Disturbance in the Ecology and Conservation of Birds Jeffrey D. Brawn, Scott K. Robinson and Frank R. Thompson III Annual Review of Ecology and Systematics , Vol. 32, (2001), pp. 251-276. Web. 4 October 2013.
- Effects of Selection Cutting on Bird Communities in Contiguous Eastern Hardwood Forests . Andrew P. Jobes, Erica Nol and Dennis R. Voigt The Journal of Wildlife Management , Vol. 68, No. 1 (Jan., 2004), pp. 51-60. Web. 4 October 2013.
- Brace, L.; Bella, I. 1988. Understanding the understorey: dilemma and opportunity. In White spruce understories. Canada–Alberta Agreement, Projects 1480, 1488, 20204. For. Can., Northern For. Centre, Edmonton AB. (Cited in Coates et al. 1994)
- Sauder, E.A. 1990. Mixedwood harvesting. section B In White spruce understories, Canada–Alberta Agreement, Projects 1480, 1488, 20204. For. Can., Northern For. Centre, Edmonton AB, various pagination.
- Sauder, E.A.; Sinclair, A.W.J. 1989. Harvesting in the mixedwood forest. Paper included in White spruce understories, Canada–Alberta Agreement, Projects 1480, 1488, 20204. For. Can., Northern For. Centre, Edmonton AB.
- Brace, L. 1989. Protecting understorey white spruce when harvesting aspen. In White spruce understories, Canada–Alberta Agreement, Projects 1480, 1488, 20204. For. Can., Northern For. Centre, Edmonton AB.
- Brace, L. 1990. A test of three logging systems in Alberta. Paper included in White spruce understories, Canada–Alberta Agreement, Projects 1480, 1488, 20204. For. Can., Northern For. Centre, Edmonton AB.
- Stewart, J.D.; Landhäusser, S.M.; Stadt, K.J.; Lieffers, V.J. 2001. Predicting natural regeneration of white spruce in boreal mixedwood understories. For. Chron. 77(6):1006–1013.
- Johnstone, W.D. 1978. Growth of fir and spruce advance growth and logging residuals following logging in west-central Alberta. Can. Dep. Environ., Can. For. Serv., Northern For. Res. Centre, Edmonton AB, Inf. Rep. NOR-X-203. 16 p.
- Ball, W.J.; Kolabinski, V.S. 1979. An aerial reconnaissance of softwood regeneration on mixedwood sites in Saskatchewan. Can. Dep. Environ., Can. For. Serv., Northern For. Res. Centre, Edmonton AB, Inf. Rep. NOR-X-216. 14 p.
- McCaughey, W.W.; Ferguson, D.E. 1988. Response of advance regeneration to releaase in the Inland Mountain West: a summary. p. 255–266 in Schmidt, W.C. (Compiler). Proc. Future Forests of the Mountain West: A Stand Culture Symp. , Sept./Oct. 1986, Missoula MT. USDA, For. Serv., Intermount. Res. Sta., Ogden UT, Gen. Tech. Rep. INT-243. 402 p.
- Stettler, R.F. 1958. Development of a residual stand of interior spruce–alpine fir during the first twenty-eight years following cutting to a 12-inch diameter limit. For. Serv., Victoria BC, Res. Note 34. 15 p. [Coates et al. 1994]
- Baskerville, G.L. 1961. Response of young fir and spruce to release from shrub competition. Can. Dep. Northern Affairs and National Resources, For. Branch, Ottawa ON, For. Res. Div., Tech. Note 98. 14 p. (Cited in Coates et al. 1994)
- McKinnon, L.M.; Mitchell, A.K.; Vyse, A. 2002. The effects of soil temperature and site preparation on subalpine and boreal tree species: a bibliography. Nat. Resour., Can., Can. For. Serv., Victoria BC, Inf. Rep. BC-X-394. 29 p.
- Kiil, A.D.; Chrosciewicz, Z. 1970. Prescribed fire – its place in reforestation. For. Chron. 46:448–451.
- Holt, L. 1955. White spruce seedbeds as related to natural regeneration. Pulp Paper Res. Instit. Can., Montreal QC. 28 p.
- Tarrant, R.F. 1954. Effect of slash burning on soil pH. USDA, For. Serv., Pacific Northwest For. and Range Exp. Sta., Portland OR, Res. Note 102. 5 p.
- Taylor, S.W.; Feller, M.C. 1987. Initial effects of slashburning on the nutrient status of Sub-boreal Spruce Zone ecosystems. In Papers presented at the Fire Management Symposium, April 1987, Prince George BC, Central Interior Fire Protection Committee, Smithers BC.
- Little, S.N.; Klock, G.O. 1985. The influence of residue removal and prescribed fire on distribution of forest nutrients. USDA, For. Serv., Res. Pap. PNW-333.
- Endean, F.; Johnstone, W.D. 1974. Prescribed fire and regeneration on clearcut spruce–fir sites in the foothills of Alberta. Environ. Can., Can. For. Serv., Northern For. Res. Centre, Edmonton AB, Inf. Rep. NOR-X-126. 33 p.
- Kiil, A.D. 1965. Weight and size distribution of slash of white spruce and lodgepole pine. For. Chron. 41:432–437.
- Kiil, A.D. 1968. Weight of the fuel complex in 70-year-old lodgepole pine stands of different densities. Department of Forestry and Rural Development, Forest Research Laboratory, Calgary, Alberta. Departmental Publication 1228. 13 p.
- Ronco, F. 1975. Diagnosis: sunburned trees. J. For. 73(1):31–35. (Cited in Coates et al. 1994).
- Wang, G.G.; Siemens, A.; Keenan, V.; Philippot, D. 2000. Survival and growth of black and white spruce seedlings in relation to stock type, site preparation and plantation type in southeastern Manitoba. For. Chron. 76(5):775–782.
- Hall, J. 1970. Site preparation in Ontario. For. Chron. 46:445–447.
- Draper, D.; Binder, W.; Fahlman, R.; Spittlehouse, D. 1985. Post-planting ecophysiology of Interior spruce. Interior Spruce Seedling Performance: State of the Art. Northern Silvic. Committee, Prince George BC. 18 p. (mimeo).
- Burton, P.; Bedford, L.; Goldstein, M.; Osberg, M. 2000. Effect of disk trench orientation and planting spot position on the ten-year performance of lodgepole pine. New For. 20:23–44.
- Clausen, J.C.; Mace, A.C., Jr. 1972. Accumulation and snowmelt on north–south versus east–west oriented clearcut strips. Univ. Minnesota, Coll. For., St. Paul MN, Minn. For. Res. Notes No. 34. 4 p.
- Daniel, T. W., J. A. Helms, and F. S. Baker 1979. Principles of Silviculture, 2nd Edition. McGraw-Hill, New York. 521 pp. ISBN 0-07-015297-7
- Evans, J. 1984. Silviculture of Broadleaved Woodland. Forestry Commission Bulletin 62. HMSO. London. 232 pp. ISBN 0-11-710154-0
- Hart, C. 1995. Alternative Silvicultural Systems to Clear Cutting in Britain: A Review. Forestry Commission Bulletin 115. HMSO. London. 93 pp. ISBN 0-11-710334-9
- Nyland, R. D. 1996. Silviculture, Concepts and Applications. The McGraw-Hill Companies, Inc. New York. 633 pp. ISBN 0-07-056999-1
- Nyland, R. D. 2002 Silviculture: Concepts and Applications, 2nd Edition. The McGraw-Hill Companies, Inc. New York. 704 pp. ISBN 0-07-366190-2
- Savill, P., Evans, J., Auclair, D., Falck, J. 1997. Plantation Silviculture in Europe. Oxford University Press, Oxford. 297 pp. ISBN 0-19-854909-1
- Smith, D. M. 1986. The Practice of Silviculture, 8th edition. John Wiley & Sons, Inc., New York. 527 pp. ISBN 0-471-80020-1
- Smith, D. M., B. C. Larson, M. J. Kelty, P. M. S. Ashton. 1997. The Practice of Silviculture: Applied Forest Ecology, 9th edition. John Wiley & Sons, New York. 560 pp. ISBN 0-471-10941-X
- Reid, R. (2006) 'Management of Acacia melanoxylon in Plantations' 
- Reid, R. (2002) 'The Principles and Practice of Pruning'