Uneven-age Stand Management. a.k.a. Uneven-aged (Sized) Silviculture Walt Wintturi- Watershed to Wildlife

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Uneven-age Stand Management a.k.a. Uneven-aged (Sized) Silviculture Walt Wintturi- Watershed to Wildlife

Define Terms Review Concepts

Uneven-age Stand At least three distinct age classes irregularly mixed in the same area. Well defined differences in total height and age, not just diameter.

Uneven-age Stand Structure Uneven-age Stand Structure 80 70 60 50 Trees per Acre 40 30 20 10 0 6 8 10 12 14 16 18 DBH

Contrast to Even-age Stand Structure Even-age Stand Structure 40 35 30 25 Trees per Acre 20 15 10 5 0 4 6 8 10 12 14 16 DBH

Stand Height vs. Time Stand Height vs. Time 70 60 50 Height (Ft) 40 30 U E 20 10 0 Time (years)

Trees per Acre vs. Time Trees per Acre vs. Time Trees per Acre UM E Time

Does stand need to be uneven-age to manage it under the selection system?

Place of Uneven-aged Stands. Four reasons for developing them. 1) Stands were inherited. Cut too many young trees if stand is replaced by clearcutting. 2) Management objective requires stand always has some large trees. Aesthetic considerations. 3) Develop or maintain winter cover for wildlife. 4) Habitat type is best suited for growing shade tolerant species, i.e. enriched, sugar-maple beech fine till, softwood wet or dry pan.

Stand Size How large does an area have to be to be considered a stand? How small an area do you want to keep records for or a stand history for? Ten acres anything less is an inclusion within a stand.

Uneven-age Stand Small, irregular, even-aged groups. Groups intermixed, not clearly separated. Treated as uneven-aged from organizational standpoint.

Selection System Term applied to silvicultural program aimed at developing or maintaining an uneven-aged stand. Includes periodic harvesting. Well suited to shade tolerant species; sugar maple, beech, red spruce, balsam fir.

Selection System - continued Mature trees are removed as individuals or small groups at relatively short intervals. Time between intervals depends on growth rates, stand condition, size (value) of desired harvest.

Q factor A measure expressing stand structure. Diameter distribution diminution quotient ex. 12 trees/acre 10 class 9 trees/acre 12 class Q factor is 12/9 = 1.3

Stand Q Calculation DBH Trees/Acre Q 4 110.1 6 56.6 1.9 8 22.9 2.5 10 12.0 1.9 12 10.2 1.2 14 5.1 2.0 16 5.6 0.9 18.3/13 = Stand Q 1.4 18 4.0 1.4 20 3.2 1.2 22 1.9 1.7 24 0.8 2.2 26 1.0 0.8 28 0.8 0.3 28+ 2.3 0.3 Total 18.3

Comparing Q Factors Comparing Q's 250 200 Trees per Acre 150 100 Q 1.7 Q 1.5 Q 1.3 50 0 4 6 8 10 12 14 16 18 20 22 24 DBH

Comparing Q Factors Comparing Q's Log Scale 1000 100 Trees per Acre Q 1.7 Q 1.5 Q 1.3 10 1 4 6 8 10 12 14 16 18 20 22 24 DBH

Choosing a Structural Goal Existing stand Q. Rates of growth Stand basal area Size to which trees are to be grown. Species

Choosing a Structural Goal Choose a Q the same or slightly lower than the existing Q. Q factor is mathematical, not biological. It is a guide. Be flexible.

Must make inventory of the stand before marking it for cutting. Need to determine distribution of diameter classes by basal area. Cut is made on the basis of a comparison between actual distribution to what is assumed to be balanced.

Selection System Prescriptions used to regenerate uneven-age stands. Individual or single tree selection Development of even-aged groups of trees in very small, scattered openings. Species regenerated and perpetuated are very shade tolerant. Ex. Sugar maple & beech, spruce/fir, hemlock. Openings need to be continually enlarged to perpetuate young tree growth.

Selection System continued Group selection More feasible way of managing uneven- aged stands. Groups are 2X height of mature trees (75 ) 2x75 =150 Regeneration of some shade intolerant species. Paper birch, yellow birch, aspen.

Selection System continued Improvement cut Applied to pole timber stands. Improve residual stand quality by removing unacceptable growing stock and lower quality overstory stems.

Marking Priority 1) High risk trees 2) Undesirable growing stock 3) Trees greater than maximum diameter. 4) Slow growing trees. 5) Undesirable species. 6) Trees whose removal improves residual tree spacing.

Summary Silviculture is local. Q factor selected and maximum tree size determined by site. Diameter distribution is determined by the biology (ecology) of the forest and purposes of management and not by mathematics. No reason to have a balanced stand, work with what you have.

Summary continued With any approach to uneven-age management it is crucial to sustained yield to keep cutting openings in stands for recruitment of new regeneration. Selection system is complex requiring sophisticated prescriptions. Prescriptions take time, 3 to 4x more time.