EFFECTS OF CLEARCUTTING AND SOIL MIXING ON SOIL PROPERTIES AND UNDERSTOREY BIOMASS IN WESTERN RED CEDAR AND WESTERN HEMLOCK FORESTS ON NORTHERN VANCOUVER-ISLAND, CANADA
Rj. Keenan et al., EFFECTS OF CLEARCUTTING AND SOIL MIXING ON SOIL PROPERTIES AND UNDERSTOREY BIOMASS IN WESTERN RED CEDAR AND WESTERN HEMLOCK FORESTS ON NORTHERN VANCOUVER-ISLAND, CANADA, Forest ecology and management, 68(2-3), 1994, pp. 251-261
On northern Vancouver Island in British Columbia it has been hypothesi
sed that the cultivation effect of repeated windthrow is the cause of
the higher nutrient availability in windstorm-derived, natural second-
growth stands of western hemlock and amabilis fir (the HA type), compa
red with adjacent old-growth stands of western red cedar with a smalle
r component of hemlock, and a dense understorey of the ericaceous shru
b, salal (the CH type). In 1988 an experiment was established in a cle
arcut area containing examples of these two forest types. The experime
nt was designed to simulate the effects of a broadscale windthrow by m
ixing mineral and organic horizons using a large rake attached to an e
xcavator. In this study, a range of soil physical and chemical propert
ies, and the biomass of understorey plants, were measured 4.5 years af
ter treatment in uncut, clearcut, and clearcut and mixed plots of the
two types. In the HA type, clearcutting and soil mixing decreased surf
ace organic matter and moisture content, and increased the rate of dec
omposition of cellulose. It had little effect on the rate of microbial
activity measured using CO2 evolved in laboratory incubation, or N an
d P measured after KCl extraction, anaerobic incubation, or using ion-
exchange resin bags in situ. In the CH type, the treatment decreased m
ineralisable N and phosphate-P held on resin bags, and the rates of ce
llulose decomposition and CO2 evolution. Mixing markedly decreased the
cover of salal compared with both the clearcut only and the uncut tre
atment. The anticipated benefits of mixing and soil disturbance (incre
ased soil nutrient availability brought about by the mixing of mineral
and organic horizons) have not occurred. This was probably because th
e mixing treatment brought humus material from deeper in the soil prof
ile to the surface. Decomposition of this material is limited more by
its poorer quality for decomposers (lower N concentration, and possibl
y higher tannins) than by soil microclimate.