(a) Dense
lichen woodlands in a fire - free landscape and corresponding to 10 % of the study sites.
(b) Less dense
lichen woodlands in a landscape with fire occurring only once during the Holocene.
The longest tree - ring chronology (AD 1398 — 1982) yet available in eastern North America was constructed from living and dead spruces found in
the lichen woodland of our study.
Not exact matches
Within the dominant oak - hickory
woodlands, one finds a diversity of habitats, from rocky glades inhabited by roadrunners and cacti to wetlands with highly mineralized groundwater — all welcoming spots for
lichens to settle in myriad colors and forms.
(f)
Lichen - heath tundras caused by deforesting fire 450 years ago adjacent to fire - free lichen - spruce wood
Lichen - heath tundras caused by deforesting fire 450 years ago adjacent to fire - free
lichen - spruce wood
lichen - spruce
woodlands.
Time - since - fire of all post-fire
woodlands and krummholz and several
lichen - tundra sites was determined based on 203 radiocarbon - dated charcoal (or wood) fragments located beneath the modern organic topsoil (appendix A).
(a) Old - growth
lichen - spruce
woodland more than 2000 years old.
Given the fact that the latitudinal position of successful post-fire regeneration of
lichen - spruce
woodlands is situated approximately 1.5 ° south of the Boniface area (Payette et al. 1989a, b), as a rule of thumb it is probable that a drop of at least 1 °C in mean annual temperature occurred after 900 cal.
Lichen - spruce woodlands in black, lichen - spruce krummholz in medium grey and lichen - heath tundras in light
Lichen - spruce
woodlands in black,
lichen - spruce krummholz in medium grey and lichen - heath tundras in light
lichen - spruce krummholz in medium grey and
lichen - heath tundras in light
lichen - heath tundras in light grey.
An evaluation of the former abundance of black spruce in
lichen - tundra sites, based on distribution, number and growth form of charred standing or fallen dead stems was done in order to deduce the presence of
woodland or krummholz stands at the moment of the last fire event.
The remaining 10 % is an exceptionally fire - free area composed of old - growth,
lichen - Empetrum nigrum
woodlands and krummholz (figure 7a, b), probably much older than 3000 yr according to 14C dates of the organic matter at the base of modern organic horizons (Payette & Morneau 1993).
Spruce - moss stands are the most important forest type in depressions, whereas
lichen - spruce
woodlands and krummholz (pygmy forests; distorted spruce less than 2.5 m high) are distributed on slopes and exposed summits along with
lichen - heath - dwarf birch (Betula glandulosa Michx.)
The interpretation of radiocarbon dates of charcoal material to infer fire dates requires knowledge on the long - term dynamics of old - growth
lichen - spruce
woodlands.
Lichen - spruce woodland and lichen - spruce krummholz are two dominant vegetation types having more than 10 % spruce cover, whereas lichen - tundra is a spatially dominant vegetation type having less than 10 % spruce
Lichen - spruce
woodland and
lichen - spruce krummholz are two dominant vegetation types having more than 10 % spruce cover, whereas lichen - tundra is a spatially dominant vegetation type having less than 10 % spruce
lichen - spruce krummholz are two dominant vegetation types having more than 10 % spruce cover, whereas
lichen - tundra is a spatially dominant vegetation type having less than 10 % spruce
lichen - tundra is a spatially dominant vegetation type having less than 10 % spruce cover.
Mosaic of post-fire old - growth
woodlands and
lichen - heath tundras in the background.
We report here results of the analysis of a ∼ 600 - year response of a
lichen — spruce
woodland to this long - term trend, which are thought to be the first extensive illustration of these impacts in the Subarctic.