Very little mechanical damage was observed in the Park. Even
broken tree tops, occurring from wind stress, were found to be
less common than expected. The one exception that was observed,
albeit not a serious condition, was that some trees have experienced
some animal rub damage. A few redwood trees along the Big Trees
Trail between Areas I and J lying just
west of Skyline Boulevard have scuffed bark at two to six feet
above ground level. This condition is not uncommon in forests
where bear and often elk will return to a favorite tree to scratch
themselves. The result is often that most of the bark gets rubbed
off, and damage occurs to the underlying cambium layer. Trees
do not usually die from this; however, their growth is often retarded.
The trees observed in the Park had very light damage that was
likely caused by horses hobbled in this area by equestrian users.
This situation should be monitored in the future to insure significant
damage does not occur.
Pathogens, rots and insect infestations, are less common in redwood
than in other tree species occurring in this region. However they
do occur. Often rot causing fungus will be introduced through
a mechanical wound on a tree. The redwood trees in Joaquin Miller
Park appear more resistant than average to effects of rot. Even
where the base of a tree was observed to have damage that may
expose the tree to a fungal infection, very little to no rot was
observed. No problems with pathogens were observed.
No specific areas were observed that could be identified as significantly
different from overall conditions observed in the Park trees relative
to tree vigor, mechanical damage, or pathogens.
A total of twenty trees were bored to determine age and growth
rate. Table 3 shows tree bore data including sample location,
diameter at breast height (DBH), total height, and radial growth
increments for five year time periods. Trees were sampled in areas
F, H, I, J", and "K (Figure 1). Areas D"
and "E were found to have very few redwood trees, those
located were small saplings which were in good health and growth
status. Area G exhibited significantly lighter trail
use than other areas surveyed and was not sampled. Sample trees
were selected from the heavier use trail areas. Trees were selected
for growth measurement that were immediately adjacent to trails
and had exposed roots on the trail (see Figures 3 and 4); and
also trees located approximately 30 feet off the trail where the
tree base was unaffected by trail use compaction and disturbance,
but the tree crowns essentially occupy the same space as the trail
adjacent trees.

