Tgf. Kittel et al., Global and regional modelling of Arctic-boreal vegetation distribution andits sensitivity to altered forcing, GL CHANGE B, 6, 2000, pp. 1-18
Understanding the distribution and function of Arctic and boreal ecosystems
under current conditions and their vulnerability to altered forcing is cru
cial to our assessment of future global environmental change. Such efforts
can be facilitated by the development and application of ecological models
that simulate realistic patterns of vegetation change at high latitudes. Th
is paper reviews three classes of ecological models that have been implemen
ted to extrapolate vegetation information in space (e.g. across the Arctic
and adjacent domains) and over historical and future periods (e.g. under al
tered climate and other forcings). These are: (i) equilibrium biogeographic
al models; (ii) frame-based transient ecosystem models, and (iii) dynamic g
lobal vegetation models (DGVMs). The equilibrium response of high-latitude
vegetation to scenarios of increased surface air temperatures projected by
equilibrium biogeographical models is for tundra to be replaced by a northw
ard shift of boreal woodland and forests. A frame-based model (ALFRESCO) in
dicates the same directional changes, but illustrates how response time dep
ends on rate of temperature increase and concomitant changes in moisture re
gime and fire disturbance return period. Key disadvantages of the equilibri
um models are that they do not simulate time-dependent responses of vegetat
ion and the role of disturbance is omitted or highly generalized. Disadvant
ages of the frame-based models are that vegetation type is modelled as a se
t unit as opposed to an association of individually simulated plant functio
nal types and that the role of ecosystem biogeochemistry in succession is n
ot explicitly considered. DGVMs explicitly model disturbance (e.g. fire), o
perate on plant functional types, and incorporate constraints of nutrient a
vailability on biomass production in the simulation of vegetation dynamics.
Under changing climate, DGVMs detail conversion of tundra to tree-dominate
d boreal landscapes along with time-dependent responses of biomass, net pri
mary production, and soil organic matter turnover-which all increase with w
arming. Key improvements to DGVMs that are needed to portray behaviour of a
rctic and boreal ecosystems adequately are the inclusion of anaerobic soil
processes for inundated landscapes, permafrost dynamics, and moss-lichen la
yer biogeochemistry, as well as broader explicit accounting of disturbance
regimes (including insect outbreaks and land management). Transient simulat
ion of these landscapes can be further tailored to high-latitude processes
and issues by spatially interactive, gridded application of arctic/boreal f
rame-based models and development of dynamic regional vegetation models (DR
VMs) utilizing plant functional type schemes that capture the variety of hi
gh-latitude environments.