Abstract:Primary succession to montanerain forest on the bare slip faces of landslides is described from three variously aged slides with plot and plotless data, 24 years after a previous study, and is related to adjacent mature forest. Over a 15-102 yr period striking successional changes occurred in both vegetation and flora.The dominant pioneer, Leptospermum scoparium, persists with decreasing importance in the canopy beyond a century, with regeneration falling completely from the seventh decade. Although some speci… Show more
“…He also found higher light levels, more extreme temperatures, greater moisture stress due to enhanced evapotranspiration, and continuing substrate instability on the steep upper slopes of landslide scars. Numerous recent studies have similarly reported lower nutrient levels (Reddy and Singh, 1993;Dalling and Tanner, 1995), more extreme temperatures (Mark et al, 1989), and continuing substrate instability (Hunter and Parker, 1993) on landslides relative to terrain adjacent to landslide scars. Many have reported a predominance of pioneer species on landslide scars (e.g., Miles and Swanson, 1986;Guariguata, 1990;Simon et al, 1990;Mark et al, 1989); on sites characterized by repeated failure, pioneers may dominate indefinitely (Orme, 1990;cf.…”
Section: Slopes Affected By Slope Failure and Mass Movementmentioning
confidence: 85%
“…These findings suggest that revegetated landslides may greatly affect the land scape-scale diversity of forested mountain environments. Most scholars tracking revegetation of scars over time have reported predictable successional changes in composition and structure (Johnson, 1976;Hupp, 1983;Mark et al, 1989). Because of inherent variation among different scars (Flaccus, 1959;Miles and Swanson, 1986;Guariguata, 1990), however, revegetation patterns revealed by chronosequences of landslide scars often are less detailed and predictable.…”
Section: Slopes Affected By Slope Failure and Mass Movementmentioning
confidence: 97%
“…Contrasts in plant species composition and physical charac teristics are often apparent between landslide scars and the surrounding vegeta tion (e.g., Mark et al, 1989;Veblen and Ashton, 1978;Miles et al, 1984;Simon et al, 1990;Reddy and Singh, 1993), although considerable spatial variation in plant cover and physical variables also is evident within landslide scars. In the White Mountains of the northeastern United States, Flaccus (1959) reported lower organic matter content and available calcium, magnesium, and potassium in soils on landslide scars than in the adjacent forest.…”
Section: Slopes Affected By Slope Failure and Mass Movementmentioning
“…He also found higher light levels, more extreme temperatures, greater moisture stress due to enhanced evapotranspiration, and continuing substrate instability on the steep upper slopes of landslide scars. Numerous recent studies have similarly reported lower nutrient levels (Reddy and Singh, 1993;Dalling and Tanner, 1995), more extreme temperatures (Mark et al, 1989), and continuing substrate instability (Hunter and Parker, 1993) on landslides relative to terrain adjacent to landslide scars. Many have reported a predominance of pioneer species on landslide scars (e.g., Miles and Swanson, 1986;Guariguata, 1990;Simon et al, 1990;Mark et al, 1989); on sites characterized by repeated failure, pioneers may dominate indefinitely (Orme, 1990;cf.…”
Section: Slopes Affected By Slope Failure and Mass Movementmentioning
confidence: 85%
“…These findings suggest that revegetated landslides may greatly affect the land scape-scale diversity of forested mountain environments. Most scholars tracking revegetation of scars over time have reported predictable successional changes in composition and structure (Johnson, 1976;Hupp, 1983;Mark et al, 1989). Because of inherent variation among different scars (Flaccus, 1959;Miles and Swanson, 1986;Guariguata, 1990), however, revegetation patterns revealed by chronosequences of landslide scars often are less detailed and predictable.…”
Section: Slopes Affected By Slope Failure and Mass Movementmentioning
confidence: 97%
“…Contrasts in plant species composition and physical charac teristics are often apparent between landslide scars and the surrounding vegeta tion (e.g., Mark et al, 1989;Veblen and Ashton, 1978;Miles et al, 1984;Simon et al, 1990;Reddy and Singh, 1993), although considerable spatial variation in plant cover and physical variables also is evident within landslide scars. In the White Mountains of the northeastern United States, Flaccus (1959) reported lower organic matter content and available calcium, magnesium, and potassium in soils on landslide scars than in the adjacent forest.…”
Section: Slopes Affected By Slope Failure and Mass Movementmentioning
“…Landslides are more infrequent than tree fall disturbances (Garwood 1979), but the scale is larger. After landslides, pioneer tree species may colonize immediately and remain for a century or more (Mark et al 1989). Brokaw (1987) showed that uncommon pioneer species, some of which are tall, long-lived species, may be vestiges of previous patterns of secondary succession.…”
The population structure and regeneration of canopy species were studied in a 4 ha plot in an old-growth evergreen broad-leaved forest in the Aya district of southwestern Japan. The 200 m x 200 m plot contained 50 tree species, including 22 canopy species, 3,904 trees (dbh > 5 cm) and a total basal area of 48.3 m2/ha. Forty one gaps occurred within the plot, and both the average gap size (67.3 m 2) and the total area of gap to plot area (6.9 %) were small. Species found in the canopy in the plot were divided into three groups (A, B, C) based on size and spatial distribution patterns, and density in each tree size. Group A (typical species: Distylium racemosum, Perseajaponica) showed a high density, nearly random distribution and an inverse J-shaped size distribution. Species in group B (Quercus salicina, Quercus acuta, Quercus gilva) were distributed contagiously with conspicuous concentration of small trees (< 5 cm dbh) around gaps. However, the species in this group included few trees likely to reach the canopy in the near future. Group C included fast-growing pioneer and shade intolerant species (e.g. Comus controversa, Carpinus tschonoskii, Fagara ailanthoides), which formed large clumps. Most gaps were not characterized by successful regeneration of group B and C but did appear to accelerate the growth of group A. Group B species appear to require long-lived or large gaps while group C species require large, catastrophic disturbances, such as landslides, for regeneration.
“…Consequently the time between disturbance and the establishment of the first tree in a cohort could vary considerably. Observations of vegetation colonisation on over twenty surfaces of known age since disturbance indicate that the first appearance of the species we include in this study takes from 3^0 years (Baxter & Norton 1989;Bray 1989;Mark et al 1989;A. Wells, unpubl.…”
Section: The Timing Of Disturbance Eventsmentioning
Mature stands of trees dominate Westland forests and young stands are relatively scarce. To examine this pattern, we collate previously-gathered data on the age and diameter of trees in 60 forest stands from throughout Westland, and use these data to estimate the dates at which approximately even-aged cohorts of trees were initiated by major disturbances. The ages of the oldest tree in each of 80 cohorts were combined to give a picture of the timing of cohort establishment and the history of major disturbance in the Westland region.We identified two periods of greatly increased cohort establishment in the last 600 years, at c. 200-300 and 500-550 years ago. During these periods over 70 % of the cohorts we examined were initiated. These establishment periods were consistent across all six canopy species in the study, throughout north, central, and south Westland, and across a range of landforms. Our results suggest there have been two major pulses of tree regeneration in Westland over the last 600 years, although the longer and most recent pulse may reflect two separate pulses. Many cohorts contained independent evidence of a catastrophic origin following major disturbances such as floods and landslips, and we suggest that the pulses of cohort establishment reflect periods when there was a marked increase in the frequency or intensity of major natural disturbances throughout Westland. Adjusting for the time taken for trees to grow to coring height and for a delay in colonisation following disturbance, we estimate that there were episodes of major natural disturbance throughout Westland around 250-350 and 550-600 years ago. These dates closely coincide with estimates of the timing of two of the three last major movements of the Alpine Fault, and less closely coincide with inferred nationwide periods of increased storminess.
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