Methods of Analyzing Vegetation Change Part One: A brief
introduction to inference from stand structure
Possible objectives:
Regeneration status (persistent or not persistent)
Regeneration mode
Reconstruction of stand history
Prediction of future composition
Required information:
1. The species pool and where species "segregate out along environmental
gradients" (i.e. which species can tolerate a particular site).
2. Basic autecological information such as dispersal mechanisms, vegetative
reproduction, longevity, seed production and periodicity, etc.
3. Quantitative data on stand structure
Types of data collected:
i. tree population age structures (sometimes supplemented with size
data)=the basic data
ii. tree spatial patterns (clumping, associations of size/age classes by
species and micro-site)
iii. disturbance history (documentary, photographic, dendroecological, etc.)
iv. understory data (interference from non-tree species, seedling
abundances and micro-sites)
v. tree canopy structure (density, cover; estimated or measured)
vi. vertical structure (relative tree heights; emergent, dominant, suppressed,
etc.)
Types of Age Structures
Types of age structures include even-aged versus uneven-aged. The uneven-aged
class is further divided into intermittent (sporadic), uniform, or “balanced” age structures.
See the discussion of this in Veblen 1992.
Limitations to Age Structure Analysis
A. Confusion of variation in past mortality and past recruitment rates.
Static-age structure curves (frequency distributions of numbers of trees in age
classes) are shaped both by variations in past recruitment (e.g., past “pulses” of
recruitment) and past mortality (e.g., effects of a past drought). This is the fundamental
reason why static-age structure curves are not the same as a survivorship curve
determined from a fixed cohort life table; tree mortality rates cannot be derived from
static-age structure.
B. Errors in determining tree ages:
1. Ring-counting errors.
2. Missed pith.
3. Time required to grow to coring height.
C. Missing age data due to rotten centers.
D. Great sampling effort required to age trees over a large area.
Limitations to size (dbh) structure analysis (i.e. substitute tree size for tree age).
Restrictions/guidelines for size structure analysis.
A. Minimize dependence on size data and maximize collection of age data.
B. Test age/dbh relationship by sampling ages of large range of tree sizes in a
uniform habitat.
C. Adjust the detail of the interpretation (and analytical procedures) according to
the strength of the age/dbh relationship. Even if there is a strong relationship between
age and dbh (e.g., correlation coefficents of 0.9) you can only make general inferences
(e.g., persistence versus non-persistence) from size structure analysis and you cannot
reconstruct the details of stand history or reach conclusions about the quantitative
stability of the population.
D. Interpret data on a stand-by-stand basis before attempting to lump data from
dispersed sample sites (likewise this is necessary in age-structure analysis). Problems
with lumping result from:
age/dbh relationship changes with site;
disturbance history changes with site;
regeneration modes become obscured;
always try to combine age/size analysis with precise dating of disturbance
events.
Substitution of Space for Time Approaches
Chronosequences
Many studies combine age structure analysis with the chronosequence approach.
A chronosequence depends on the assumption that the sites being compared are
ecologically identical and that the only variable that varies among the sites is age or time
since disturbance.
Natural experiments:
Comparison of islands/mainlands.
Comparisons of affected and unaffected sites as a substitute
for before and after the event.
What are the assumptions underlying these approaches?