DYNAMICS OF THE DEAD WOOD CARBON POOL IN NORTHWESTERN RUSSIAN BOREAL FORESTS

Citation
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
Citations number
52
Categorie Soggetti
Environmental Sciences","Water Resources
ISSN journal
00496979
Volume
82
Issue
1-2
Year of publication
1995
Pages
227 - 238
Database
ISI
SICI code
0049-6979(1995)82:1-2<227:DOTDWC>2.0.ZU;2-X
Abstract
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.