Amazonian forests play a key role in the global carbon cycle, thus increases their significance, but there is much uncertainty about the quantity and distribution of carbon stored in these forests.
The rapid conversion of tropical forests is a
major source of greenhouse gases such as carbon dioxide, methane, and nitrous
oxide, which are the principle causes of global warming (Houghton and Fearnside).
Nowhere is
deforestation occurring more rapidly than in
Brazilian Amazonia, which contains about 40% of the world's remaining tropical
rainforests ( Laurance et al., 2001a). From 1995 to 1999, deforestation
rates in the Brazilian
Amazon averaged nearly 2 million hectares per
year ( INPE, 2000), not including extensive forest areas degraded by logging,
ground fires, forest fragmentation, illegal gold-mining, and overhunting
( Skole; Laurance;
Cochrane and Nepstad).
Despite the important role of Amazonian forests
in the global carbon cycle (Fearnside, 1997a), data on biomass and carbon
storage in the region are clearly inadequate (e.g. Brown; Brown and Brown).
Biomass estimates
for Amazonian forests have been the subject of
considerable debate (e.g. Brown; Brown; Fearnside; Fearnside and Fearnside)
because of limited data, methodological differences among investigators,
and small or
incomplete measurements of biomass in some studies
(cf. Houghton et al., in press). Current estimates of total carbon storage
in Brazilian Amazonia vary by more than a factor of 2, from 39 to 93 Pg
C, largely as a result of
uncertainty in the quantity and spatial distribution
of forest biomass ( Houghton et al., in press). Houghton et al. (2000)
concluded that 60% of the uncertainty in their estimates of annual carbon
flux from Brazilian
Amazonia resulted from varying estimates of forest
biomass. Clearly, there is a need for additional measurements of biomass
across large expanses of the Amazon basin.
In a recent study, Laurance et al. (1999) assessed the relationship between soil features and aboveground biomass of live trees for 65 1 ha plots arrayed across an extensive (ca. 1000 km2) central Amazonian landscape.
Biomass estimates in this study were generated
by measuring diameters of all large (10 cm diameter-at-breast-height (DBH))
trees and then using a correction factor to approximate biomass of small
(<10 cm DBH)
trees. Here we provide a much more comprehensive
estimate of aboveground biomass for the same study area, based on 20 randomly
selected 1 ha plots in which biomass of all live and dead material (large
trees, small
trees, seedlings, palms, lianas, downed wood
debris, snags, litter, aboveground root mat) was quantified.
And.. the results after various testing methods..
whcih ill probably put up later.
A key conclusion is that biomass in these forests is very high, averaging nearly 400 Mg ha-1
Collectively, these studies illustrate the high
capacity of intact Amazonian forests for carbon storage. Assuming that
50% of biomass is carbon, aboveground carbon storage in our study area
is nearly 200 Mg ha-1, with
perhaps another 35¯40 Mg ha-1 as belowground
biomass and roughly 300 Mg ha-1 as soil organic matter. Forest conversion
is unlikely to have major effects on deep soil organic matter, but it can
dramatically reduce
carbon storage aboveground and in the roots and
upper soil layers
Amazon forests contain a very large stock of terrestrial
carbon (Fearnside and Houghton) and are probably an important carbon sink
( Grace; Phillips; Malhi and Chambers). Thus, understanding the spatial
distribution of
biomass in these forests is an urgent priority.
Carbon storage in undisturbed forests is very high, suggesting that forest
conversion is likely to be an even larger source of greenhouse gas emissions
than previously anticipated. This is important because plans are well underway
to expand networks of highways, railroads, gas lines, and other major infrastructure
projects in the Brazilian Amazon. By opening large expanses of the basin's
remote interior to exploitative activities, these projects are predicted
to sharply accelerate the pace of forest conversion and degradation ( Carvalho
and Laurance). Agricultural practices in the Amazon are limited by very
low soil fertility ( Kauffman and Fearnside), and the economic value of
intact forests for carbon storage, biodiversity conservation, and other
natural ecosystem services may ultimately be far greater than that provided
by forest conversion.