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decay of aspen and balsam poplar in alberta - Canadian Forest ...

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12<br />

Table 3. Age-<strong>decay</strong> relationships <strong>in</strong> <strong>balsam</strong> <strong>poplar</strong> st<strong>and</strong>s <strong>in</strong><br />

Alberta<br />

Percentage <strong>decay</strong><br />

Age class Lesser Slave Lake Rocky-Clearwater<br />

(years) 1958a 1977b,c forestsd 31-40 2. 9<br />

41·50 8.7<br />

51·60 8. 2<br />

61·70 7.4<br />

71·80 8. 4<br />

81·90 10.1<br />

91·100 11.4<br />

101·110 13.3<br />

111·120 15.2<br />

121·130 l7.3<br />

131·140 19.4<br />

141·150 21.3<br />

151·160 22.9<br />

161·170 24.5<br />

171·180<br />

a Paul <strong>and</strong> Etheridge (1958),<br />

b Bailey <strong>and</strong> Dobie (1977).<br />

C Preselected logs.<br />

d Pedology Consultants (1982).<br />

<strong>in</strong> percentage <strong>decay</strong> <strong>in</strong> several <strong>in</strong>stances. Components <strong>of</strong><br />

the same clone occupy<strong>in</strong>g two dist<strong>in</strong>guishable sites did<br />

not differ significantly <strong>in</strong> percent <strong>decay</strong> <strong>in</strong> any <strong>of</strong> the<br />

clones harvested, but considerable differences <strong>in</strong> gross<br />

volumes <strong>and</strong> <strong>decay</strong> volumes were observed between<br />

clones. In one study (Wall 1969), the <strong>in</strong>cidence <strong>of</strong> P.<br />

tremulae among <strong>in</strong>term<strong>in</strong>gled clones on the same site<br />

varied from 12% to 64%; on another site the variation<br />

ranged from 21 % to 92%.<br />

6. 2<br />

5.0<br />

5.5<br />

7.4<br />

The above observations <strong>in</strong>dicate that the genetic<br />

orig<strong>in</strong> <strong>of</strong> <strong>aspen</strong> is more important than site quality. When<br />

<strong>aspen</strong> <strong>and</strong> <strong>poplar</strong> utilization become economically attrac­<br />

tive, the identification <strong>of</strong> genetically healthy <strong>aspen</strong> clones<br />

will be important <strong>in</strong> regeneration programs (Steneker<br />

1976; Steneker <strong>and</strong> Wall 1970).<br />

<strong>poplar</strong>.<br />

No published work is available on clones <strong>of</strong> <strong>balsam</strong><br />

CULL ESTIMATION WITH EXTERNAL INDICATORS<br />

Attempts have been made to f<strong>in</strong>d a method to<br />

predict- relative <strong>in</strong>cidence <strong>and</strong> extent <strong>of</strong> <strong>decay</strong> before<br />

harvest<strong>in</strong>g is planned. Most <strong>of</strong> the published work uses<br />

external <strong>in</strong>dicators such as sporophores (ma<strong>in</strong>ly conks <strong>of</strong><br />

P. tremuiae, Fig. 8), rotten knots, <strong>and</strong> ma<strong>in</strong> stem scars<br />

(Figs. 10, 17·20) (Bailey 1974; Bailey <strong>and</strong> Dobie 1977;<br />

Basham 1958; Riley <strong>and</strong> Biers 1936) to predict <strong>decay</strong> <strong>in</strong><br />

the tree stems. Balsam <strong>poplar</strong> does not produce fruit<strong>in</strong>g<br />

bodies <strong>of</strong> P. tremulae easily, <strong>and</strong> external <strong>in</strong>dicators <strong>of</strong><br />

<strong>decay</strong> are ma<strong>in</strong>ly ,rotten knots <strong>and</strong> large scars (Fig. 10).

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