On. Krankina et Me. Harmon, DYNAMICS OF THE DEAD WOOD CARBON POOL IN NORTHWESTERN RUSSIAN BOREAL FORESTS, Water, air and soil pollution, 82(1-2), 1995, pp. 227-238
Our study examines dead wood dynamics in a series of permanent plots e
stablished in closed, productive second-growth forest stands of north-
west Russia and in temporary plots that represent different succession
al stages and types of disturbance. Dead wood stores measured on 63 pl
ots 0.2-1.0 ha in size range from 1-8 Mg C ha(-1) in young to mature i
ntensively managed stands, 17 Mg C ha(-1) in an old-growth forest, 20
Mg C ha(-1) on a clear-cut, and 21-39 Mg C ha(-1) following a severe w
indthrow. A total of 122 logs, snags, and stumps aged by long-term plo
t records was sampled for decay rates and to develop a system of decay
classes. Annual decomposition rates are: 3.3% for pine, 3.4% for spru
ce, and 4.5% for birch. Based on these decay rates the average residen
ce time of carbon (C) in the dead wood pool is 22-30 years. The mortal
ity input on the permanent plots was 23-60 Mg C ha(-1) over 60 years o
f observation or 15-50% of the total biomass increment. This data sugg
ests a dead wood mass of 10-22 Mg C ha(-1) would be expected in these
mature forests if salvage had not occurred. In old-growth forests, dea
d wood comprised about 20% of the total wood mass, a proportion quite
similar to the larger, more productive forests of the Pacific Northwes
t (USA). If this proportioning is characteristic of cool conifer fores
ts it would be useful to estimate potential dead wood mass for old-gro
wth forests without dead wood inventories. However, the use of a singl
e live/dead wood ratio across the range of successional stages, a comm
on practice in C budget calculations, may substantially over- or under
-estimate the dead wood C pool depending upon the type of disturbance
regime. Intensive forest management including short harvest rotations,
thinning and wood salvage reduces dead wood C stores to 5-40% of the
potential level found in undisturbed old-growth forest. In contrast, n
atural disturbance increases dead wood C pool by a factor of 2-4.